Wednesday, May 20, 2015

Kelp Farming and Ice Dyking

Aaron Franklin
Kelp farming and ice dyking for habitat enhancement 
and carbon-negative fuels and chemical production.

By Aaron Franklin

A purpose-built craft like this Ground effect plane / hovercraft triphibian concept could be ideal.

The laterally-rigid sideskirts with vertically-flexible surface-contouring ski bottoms would allow transitions between air, water, ice, snow, earth surfaces of all types and the waterscoop tail could directly hose the water onto the ice with foil effect to counter lateral reaction thrust. Snow making, firefighting, and ecology seeding also in its functionality.

At pumping of 10tons per second, 50m x 100m/s = 5000sqm, 10000kg/5000sqm = 2 kg per sqm per pass. About 2mm per pass.

If we assume conditions that will allow 2 mm to freeze in 30 seconds. then 4mm per minute = 240mm per hour = 5760mm (near 6m thick) per day could be made of 50m wide by 100m/s x 30s = 3km long of icedyke by a mobile spray vehicle at 100m/s.

3000m x 6m x 50m = 900 000 tons per day of ice making.

A fleet of 50 working for 100 days therefore could make 5000 x 900 000 = 45 000 000 000 tons or near 5 cubic kilometers of ice. 

If we are looking at an average needed to ground them of say 30m thick, then 50m wide is cross section area of 1500 sqm.

5 000 000 000 cubic m / 1500 sqm = 3.33333 million meters or 3333 km.

A ball park figure of 1000kw vehicle power would seem adequate to do this.

Very likely a rope mesh reinforcement would need to be floated on the water and anchored in place to hold together the dyke that has been formed. Doing this work in polynyas seems the best way, then towing into position of sections to be anchored and further thickened.

If 100 such vehicles were used you've got near seven thousand km of icedyke which could be enough for such a layout as this:
Kelp farming, by Aaron Franklin, on background image by Shakhova et al., 2010

For methane plume hotspots to the surface, hexagonal tiles would need to be formed and towed into place, if they are too rich for ice to form inside the rings in situ.

Stationary pumping systems might have to high costs per area in most places with limits to small volumes per pump due to area feasible to distribute the water to and ice layup rates. Though in saying this, high cost is often seen as a benefit for commercial interests. They can make more money doing it the hard way.

The purposes of kelp farming in the less methane emissive areas is as follows:
  • Biomass for biofuels and biochemicals of around 500 ton per hectare per year can be harvested.
  • The growing kelp oxygenates the water to support consumption of methane and river in-flux of organic carbon.
  • The artificial kelp forests provide habitat and food for a diverse and rich ecology with fisheries and abalone/ mussel/ crabs / lobster etc farming potential
  • Unlike micro algae, the kelp biomass is easily harvested, so it would not rot and cause oxygen depletion of the water at the end of summer.
  • Sedimentation rates and water clarity are vastly improved by the kelp forests, thereby improving albedo and enhancing natural carbon burial in sediments.
  • Simple and low cost infrastructure only is neccessary to process the kelp locally into liquids for low transport costs to refineries for further upgrading.
  • It would be easy to use the CO2 from an initial biomass pyrolysis to convert methane collected nearby to methanol for easy low cost transportation.
Combining these systems would allow zero carbon emission liquid fuels via the energy component of the fossil methane and biomass being used as hydrogen and the carbon turned into biochar and high performance bioglues and recyclable polymers, allowing further long-term carbon sequestration by wood, biofibre, etc., and component for construction materials, also replacing high carbon-emission steel, concrete etc.

Sunday, April 26, 2015

Save the Arctic

by Renaud de Richter


- This idea was proposed by Denis Bonnelle,
'Solar Chimney, water spraying Energy Tower, and linked renewable energy conversion devices: presentation, criticism and proposals', p120-125.
PhD thesis 9 July 2004, university Claude Bernard, Lyon, France, registration n°129-2004.

- For more ideas, see: 
Fighting global warming by climate engineering: Is the Earth radiation management and the solar radiation management any option for fighting climate change?
By Tingzhen Ming, Renaud de_Richter, Wei Liu and Sylvain Caillol

Friday, August 15, 2014

Seven Ocean Fertilization Strategies

by William S. Clarke

Buoyant, long-­lasting flakes can release nutrients slowly, avoiding nutrients waste and allowing balanced marine ecosystems to develop over a period of about one year. The flakes can be blown from ships’ holds to cover large ocean surfaces.

Global biosphere—the ocean's long-term average phytoplankton chlorophyll concentration between September 1997 and August 2000 combined with the SeaWiFS-derived Normalized Difference Vegetation Index over land during July 2000.

Seven different strategies have been identified that use these flakes.

1. Phosphate-­rich, but iron- and silica-deficient areas of the global oceans south of 42° South, together with some Arctic and sub-­Arctic waters, can be addressed with buoyant flakes carrying ultra-­slow-­release iron and silica minerals to generate albedo increase, marine biomass and carbon biosequestration.

2. The highly stratified and nutrient-­impoverished seas of the Caribbean and many tropical waters may be addressed using flakes bearing a mix of nutrients, chief of which are phosphate wastes (from Florida, Morocco and Australia), iron, silica and trace elements. Whilst this provision should help to transport dissolved inorganic carbon (DIC) somewhat deeper into the highly stratified sea by the oceanic carbon pump, its main functions will be to generate increased albedo (reflectiveness) of both the ocean surface and of the marine clouds above it;  to generate additional marine biomass; and to make some contribution to reducing ocean acidification, ocean surface temperature and consequently hurricane strength.

3. Some favorable tropical locations, where there are frigid currents running beneath the surface, may use Ocean Thermal Energy Conversion (OTEC) pumping mechanisms to generate power, potable water and the uplifted, nutrient-rich waters needed to fertilize mariculture operations.

4. The temperature/nutrient/salinity stratified waters of the Gulf of Mexico, with their excessively-­‐nutriated benthic waters (from the Mississippi) and often impoverished surface waters, together with other oceans where the needed nutrients can be found in deeper water, are probably best addressed by wave or wind powered pumping mechanisms. These bring nutrients to the nutrient-­‐deficient surface where they can be used by phytoplankton and in cultivated macrophyta (kelp and sargassum) forests. The process also tends to cool the warm surface water by mixing it with cooler water from the depths and by increased solar reflection.

5. Fertilizing polar waters with buoyant flakes, that include in the fertilizer mix minerals containing tungsten, cobalt, nickel and molybdenum (Glass et al. 2013) plus possibly gypsum (calcium sulfate) and seed methanotrophs (methane eaters), could play a vital part in converting huge and potentially catastrophic methane emissions occurring there into less hazardous CO2 which may itself then be converted into biomass by fertilized phytoplankton. These trace elements, but the tungsten in particular, are necessary for the production of metalloenzymes that catalyze the anaerobic oxidation of methane. Other methanotrophs would oxidize more methane aerobically in the water column above the anaerobic sediments.

6. Temperate oceans will each need to be treated differentially, depending on the mix of the nutrient concentrations already in their water columns and what can be used there near the surface by phytoplankton and macrophyta.

7. Productive ocean areas, coral reefs, seagrass meadows, and most inshore waters should typically not be treated at all, except conceivably when there are seasonal or otherwise temporary nutrient deficiencies that might beneficially be offset by the use of nutritive flakes. In many ocean regions, different combinations of these methods will be optimal.

Strategy 5. is described in more detail below.

Biological Control of Arctic Methane Emissions

Methane bubbles from: Sauter et al. 

As the Arctic Ocean seabed, tundra, and the frozen methane clathrates they contain warm, increasingly large clouds of methane bubbles have been observed ascending in pools and seawater. If these cannot be contained or converted, they are likely to cause catastrophic global warming within the expected lifetime of our children.

Reducing our carbon dioxide and methane emissions dramatically is no longer sufficient to avoid this from happening. Our two best chances are either to have the issuing methane captured and converted into something more benign, or to cool the Arctic quickly. Both appear to be daunting tasks. However, both may still be feasible. This paper focuses upon using biological means to convert the issuing methane into biomass.

Methanotrophic (methane eating) bacteria can do this using one of two metabolic pathways, aerobic or anaerobic. The aerobic route oxidises methane into methanol or formaldehyde that is then transformed into biomass. In the anaerobic route typically used by bacteria resident in ocean sediments, consortia of archaea and nitrite- or sulphate-reducing bacteria produce both biomass and carbon dioxide from methane (source: Wikipedia ‘Methanotroph’). Both routes use enzymes that contain essential metal atoms that are typically in short supply there. The metals include tungsten, copper, nickel, cobalt and molybdenum (Glass et al. 2013).

It is proposed that there be modelling, and subsequent testing, to establish optimal parameters for buoyant flakes carrying slow-release minerals that provide a balanced ‘diet’ of these essential metals, to allow the methanotrophs to proliferate and consume most of the newly emitted methane, before it can cause excessive global warming. Where a targeted site does not contain sufficient sulphate for the sulphate-reducing bacteria, cheap and plentiful calcium sulphate (gypsum) may be added to the powdered mineral mix.

Biological solutions typically have three major advantages. First, they are a natural form of control. Second, they modulate themselves to the extent of the problem. And third, they are typically both economical and fast-acting.

It is surmised that methanotrophs cannot metabolise methane when it is in frozen form in clathrates. Similarly, the methanotrophs in water, sediment, or soil must be in intimate, and preferably prolonged, contact with their gaseous or dissolved methane food source in order for them to be able to metabolise it effectively. This is not the case when the methane has been given time to aggregate into large bubbles or to issue directly into the atmosphere via vents, fissures or eruptions. It is therefore important that the metals be sufficiently available to methanotrophs both continuously and along the entire and diverse pathways of their emission and pre-atmospheric movement. Hence, the minerals should preferably: permeate the entire water column (albeit at low concentration); be present in at least the upper layers of sediments and soils; coat the surfaces of fissures and vents; and lie on the sea ice, tundra or swamp surface, ready to be elevated to a commanding position with the water surface. The surface may be either that of the sea, or of puddles, ponds, lakes and streams that form from rainfall or from thawing ice and permafrost.

The minerals should also be able to be economically distributed to all these environments. Small, benign and buoyant flakes can do this best, as they are readily disseminated pneumatically from ship or plane, with acceptable evenness and cost, to the most inaccessible areas. As the flakes slowly release their mineral payloads into the water, dissolution, assimilation and mineral particle sinking take the needed enzymatic metals to where the methanotrophs are present and can metabolise them so that they can proliferate enough to consume the varying amounts of emitted methane.

The buoyant flakes may be formed from a suitable mixture of low-grade mineral powders and the powdered lignin ‘thermoplastic glue’ left over from the extraction of sugars from straw or woody waste that glues the mineral mix in layers, and with tiny voids, onto cereal husks. These three materials have typically been regarded as waste products, or ones of little or no commercial value – though new uses are being found for lignin. All can be regarded as renewable resources. All are available in more than sufficient quantity to fertilise the Arctic many times over. It is surmised that the flakes will last approximately a year on the ocean surface, and possibly much longer in soil and sediment.

Most of the nutrients from the flakes will presumably enter the biosphere, where they will typically recycle many times before becoming buried deep in sediment, along with the lignin. Of course, some of this newly laid down, organically-rich sediment will be re-metabolised into methane or carbon dioxide. However, these in turn will readily be converted back into biomass by the aforesaid processes.

The flakes disseminated over the Arctic Ocean may also incorporate other lacking nutrients necessary for the growth of phytoplankton, such as iron, silica and phosphate. These will have the additional benefit of cooling the Arctic by increasing its albedo (reflectiveness) by ocean surface and marine cloud brightening. The increase in phytoplankton concentrations may be necessary to ensure that any additional carbon dioxide resulting from predation upon the methanotrophs, or that from other causes of methane oxidation, is also converted into benign biomass.

For more details, contact Sev Clarke at the address below.

Copyright © 2014 Winwick Business Solutions P/L. PO Box 16, Mt Macedon, VIC 3441, Australia.

Tuesday, January 14, 2014

Six commercially-viable ways to remove CO2 from the atmosphere and/or reduce CO2 emissions

by Roelof D Schuiling and Poppe L de Boer


Almost all of the CO2 that has ever leaked out of the planet has been removed from the atmosphere and the ocean, and sustainably stored in rocks, mainly by weathering, and also in the later part of the Earth’s history by storage as organic carbon. During weathering, which is the reaction of rocks with CO2 and water, CO2 is first converted to bicarbonate solutions. In the ocean corals, shellfish, and plankton convert them to carbonate sediments, which form the ultimate sustainable storage of CO2 (Figure 1).

Figure 1. A Karst landscape in China is one of the many stores for CO2 of the world.

Six solutions

Six low-cost or financially self-supporting ways are described in which we can store large
volumes of CO2 and/or significantly diminish CO2 emissions:

  1. Nickel Farming: A switch from nickel mining, ore dressing, and nickel recovery to nickel farming by the use of nickel hyperaccumulator plants. This switch will cut down CO2 emissions because it avoids the energy-intensive steps in the nickel cycle and enhances the weathering of olivine or serpentine which captures additional CO2.
  2. Biodiesel from Diatoms: Diatoms contain approximately 50% of lipids, which makes them an ideal starting material for the production of biodiesel. They grow fast, provided they have a source of silica. They do not suffer from drawbacks of land-grown biofuel crops. They do not occupy vast tracts of land that are urgently needed for food production, and they do not require vast amounts of scarce irrigation water and fertilizer. The use of biodiesel from diatoms will reduce the CO2 emissions from fossil fuels.
  3. Quenching Forest Fires: Forest fires are the second largest emitter of CO2, after fossil fuels. It was demonstrated that quenching such fires with a slurry of serpentine powder is considerably more effective than quenching with water. This reduces the emissions of CO2 by the fires and the associated financial losses. The serpentine that was calcined by the fire reacts very fast with CO2 and water afterwards, thereby compensating part of the emitted CO2 during the fire. A better and quicker mastery over forest fires may also help to save lives.
  4. Supergreen Energy: If the heat that is released by the weathering of olivine is trapped, this would represent a huge alternative source of energy that additionally captures large volumes of CO2, hence the name supergreen energy. A basic scenario is described how this could be achieved.
  5. Coastal Protection: When olivine is used for coastal protection (breakwaters, artificial reefs, sand replenishment on beaches) this has a direct effect against ocean acidification. CO2 is absorbed as bicarbonate, and the pH of the surrounding waters rises.
  6. Olivine in High-Energy Marine Environments: Large areas of shallow seas are subjected to strong currents that can transport gravel. When olivine grit is spread on the sea floor, the grains are kept in motion and bump and rub against each other. This destroys reaction-limiting silica coatings on the grain surfaces and releases micronsized slivers that rapidly react with sea water. It is the most direct way to counter ocean acidification.

1. Nickel Farming

All mining operations have an impact on the environment. This also holds for nickel, independent of the type of ore, whether nickel laterite or nickel sulfide. Nickel laterites must be leached and nickel sulfides must be roasted and dissolved. These steps are energyintensive and polluting. These disadvantages can be reduced if part of the world nickel production is gradually replaced by a switch to nickel farming. A fairly large number of plant species from different families are known to exhibit the remarkable property that they very effectively extract nickel from nickel-rich soils and store it in their tissues (Figure 2). Soils on serpentinized peridotites often contain no more than 0.2% of nickel, but the ash of these plants may contain 10% or more of nickel, much richer than the richest nickel ores. If some NPK fertilizer is spread over nickel-rich soils and such plants are sown, these nickel hyperaccumulator plants can be harvested at the end of the growing season, and their nickel content can be recovered after ashing. Several of these plants are perennial, so they do not need to be sown every year.

Figure 2. Alyssum corsicum, a nickel hyperaccumulator.

A first estimate [1] shows that the recovery of nickel by using these plants will cost no more than the current way of nickel production. This means that all the savings on CO2 expenditure and CO2 storage are essentially cost-free. In instances where an appropriate value may be associated with the CO2 savings compared to conventional nickel production, nickel farming may economically outcompete incumbent nickel production processes.

Once such nickel hyperaccumulation systems will have been fully developed and become deployable, it is hoped that governments adopt incentive structures that oblige mining companies with nickel mining assets to conduct at least part of their businesses with these methods and that associated CO2 savings and removals are quantified and verified. In addition, because the nickel obtained from phytomining is not extracted from nickel ores but from common peridotite rocks, nickel farming will extend the lifetime of nickel ore deposits.

2. Biodiesel from Diatoms

Diatoms (siliceous algae) make up a large part of the biomass in the oceans. They consist about 50% of the lipids, which makes them an ideal raw material for the production of biodiesel. The process to make biodiesel from algae is already known. They grow fast and can outcompete their competitors in the algal world in the fight for food, provided that there is sufficient silica available in their environment. Diatoms need silica for the construction of their silica skeleton (Figure 3). An extensive discussion of the role of dissolved silica in promoting the growth of diatoms at the cost of other plankton like dinoflagellates can be found in [2].

Figure 3. Diatoms have delicate silica skeletons.
Land-grown biofuels (among others oil palm, sugarcane, sweet sorghum, soybean, maize) occupy vast tracts of land that would normally be used for food production, or land that used to be the territory of threatened species like the orangutan. They also need vast volumes of scarce irrigation water and fertilizer. This results in higher prices for these fertilizers, which will push up their price as well as the price of food.

Diatoms do not have these drawbacks, but before they can be used as an alternative source of biofuel, the problems of mass culturing and harvesting them must be solved. A large-scale mariculture of diatoms might take the following shape. An artificial lagoon can be sectioned off by a dike around a sector of shallow seawater in front of a beach section.

The beach between the low-tide mark and the high-tide mark must be covered by a layer of olivine sand with a thickness of about 0.5 m. One or more U-shaped tubes are left in the dike that connects the lagoon with the open sea, permitting the tide to reach the lagoon and to alternatively wet and drain the olivine beach. These tubes should be closed by a perforated metal plate covered with a plankton net. This would permit the exchange of water, but prevent the diatoms to be carried out of the lagoon by the ebb. The olivine will weather, and the weathering solution, including the silica that is set free during the olivine reaction, will be distributed in the lagoon. In addition, the bicarbonate that is captured during olivine weathering will be used by the diatoms for photosynthesis.

When the silica limitation is removed, diatoms will form a quasi-monoculture in the lagoon. Nutrients should, of course, be added, mainly for their ammonia and phosphate requirements. A cheap way to do this would be by the use of struvite, an ammonium-magnesium phosphate that is produced by a simple and robust technology in the treatment of organic wastes, including manure, urban waste, and urine [3]. Struvite is a slow-release fertilizer that will steadily add ammonium and phosphate to the lagoon. The addition of nutrients should be limited, however, because diatoms react to a slight starvation by raising their lipid content, which increases their value for biodiesel production. The diatom production can be increased by underwater lighting at night.

Harvesting the diatoms efficiently is a major problem. The following possibility may provide a solution. Dig a hole inside the lagoon. Dead diatoms will collect in this pit, also thanks to the fact that they are relatively heavy due to their silica skeletons. From time to time, this mass of dead diatoms can be sucked up, drained and transported to the biofuel plant.

When the culture and harvesting of vast volumes of diatoms can be successfully accomplished, this application will become financially self-supporting and will reduce CO2 emissions from the burning of fossil fuels. It can be setup in any country with marine coastlines, preferentially in dry climate zones with abundant sunshine.

3. Quenching Forest Fires

Forest fires (Figure 4) are the largest CO2 emitters after the burning of fossil fuels. Forest fires and, to a lesser extent, other forest losses account annually for about 6 Gt of extra CO2 emissions on a total of somewhat more than 30 Gt of human CO2 emission [4]. They cause every year not only huge financial losses but also the deplorable loss of human lives. Experimental fires at the test site of Brandbeveiliging BV (Fire Protection) in the Netherlands were considerably faster and completely extinguished by spraying with a suspension of serpentine powder than with plain water. Serpentinite powder from the PASEK mine in North-West Spain and from the Isomag Mine in Austria was used with equally positive results.

Figure 4. Forest fires are the second largest emitter of CO2 in the world.
Serpentine can be considered the hydrated equivalent of olivine. Huge massifs of serpentinite are formed by the interaction of olivine with hydrothermal waters and also on the ocean floor along mid-ocean ridges. Serpentinite is a soft rock and serpentine is similar to a clay mineral. Like any other clay, it can be baked into a hard, brick-like substance. When this calcined serpentine is pulverized, it turns out that the powder reacts fast with CO2 and water, considerably faster even than olivine. It would be an excellent material to rapidly remove CO2 from the atmosphere, but baking it costs a lot of energy and associated CO2 emission. So, it is a pity, but using calcined serpentine against climate change is out…, except in cases where one wants to quickly remove as much heat as possible, like in extinguishing forest fires. When serpentine slurries were tested in test fires, they not only removed a considerable amount of heat from the fire, but they displayed another property which is probably more decisive. The serpentine that was sprayed over the fire turned into a thin baked impermeable skin that prevented the access of oxygen to the burning material, and also prevented the emission of the inflammable gases from the burning wood.

So, when forest fires are raging, the spraying of serpentine slurries (almost as simple as spraying water, because a 40% serpentine slurry is still very fluid) can reduce the extent and severity of such fires. When a reduction of 10% in forest losses could be achieved worldwide, this would already be a major breakthrough, since this represents a reduction of 0.6 Gt of CO2 emissions each year.

Moreover, after extinction of the fire, the calcined serpentine will quickly react with CO2 and the first rainwater, thereby compensating part of the CO2 that was emitted by the fire. It is clear that the spraying of serpentine (serpentine powder is a cheap and ubiquitous material) is a very cost-effective way of reducing the huge financial losses from forest fires, and it holds the promise of reducing losses of life as well. It pays amply for the reduction in CO2 emission by limiting the areal extent of burnt forest and by the capture of CO2 by the reaction of the calcined serpentine afterwards. It also limits the required volumes of water considerably, which is important in hot dry summers in countries that are most vulnerable for forest fires and have only limited fresh water resources.

It should be considered whether the spraying of serpentine slurries can also be used in the containment of tunnel fires.

4. Supergreen Energy

A property of olivine weathering that is commonly overlooked is its energy production. When olivine is weathering under conditions of limited water flow, it weathers according to:

Mg2SiO4 + CO2 + H2O    Mg3Si2O5(OH)4 + MgCO3
Olivine, Carbon dioxide, Water             Serpentine,   Magnesite   

Serpentine is like a clay mineral, and magnesite is similar to limestone. It is well known that baking clays to make bricks costs a lot of energy and the same holds for burning lime to make quicklime. If we follow the reverse route and make clays and carbonates, such energy is set free. Unfortunately, weathering reactions are notoriously slow, so there are no technological applications for this energy yet, because under normal conditions this heat will be radiated or conducted away. That is a pity, because the energy that is produced by the weathering of olivine is considerable. The heat flow anomalies along the mid-ocean ridges may be due, for a large part, to the widespread serpentinization of mantle rocks when they react with infiltrating sea water [5].

In a system that is very well isolated and has a large volume-to-surface ratio, it might be possible to recover most of that energy. Rocks are excellent thermal isolators, as shown by caves. If one visits a cave in summer, it feels nice and cool, and in winter it feels pleasantly warm. This is because the surrounding rocks provide a good thermal isolation and keep the cave at a fairly constant temperature throughout the year. The larger the volume of olivine sand under good isolating conditions, the better it will be able to develop and keep a high temperature. One might say, volume stands for heat production and surface area stands for heat loss; thus, the larger the volume (and the thicker the isolation), the lesser the heat loss.

A scenario that provides these conditions could be the following. An existing 550-m deep lignite mine in Germany (Figure 5) will be taken as an example; but in fact, any deep open pit mine could serve, whether in operation or left as a scar in the landscape after closure .

Figure 5. A lignite mine in Germany.
The lignite mining goes on at the front end of the mine, while the mined-out rear part is filled with the overburden that was first removed to reach the lignite seams. This way the mine moves slowly through the landscape. Villages are torn down in front of the mine and rebuilt at the backside. Instead of refilling the whole mine with the overburden, the lower 250 m may be filled with olivine sand and then topped off with the remainder of the overburden. This setup provides thermal isolation and also sufficient counter-pressure to maintain the pore waters in a liquid state. Before doing this, a network of perforated pipes and heat exchangers should be installed in the olivine sand, through which water (or steam) and CO2 can be injected. A set of thermistors inside the olivine mass will make it possible to follow its thermal evolution.

As long as the temperature is low, the reaction will be slow. In order to kickstart the process, it is advisable to first inject steam to heat the inside of the mass. This will increase the reaction rate, and as the reaction takes off, the temperature will rise further and the reaction accelerates.

When the system has reached a sufficiently high temperature to be of interest for power production, water is passed through the heat exchangers and converted to high-pressure steam.

It should be evident that such a system will require a lot of additional and rather unusual engineering before it can be operational. On the other hand, the potential reward is huge because it represents an almost unlimited amount of energy. This energy is called supergreen energy because it does not produce CO2, but, on the contrary, it traps it in a safe and solid form. The question asked by the author in [6] is relevant ‘So what would we prefer, a CCS infrastructure that uses a quarter of a power station’s electricity to sequester its CO2 emissions under the North Sea or one that generates additional electricity and useful materials products?’.

A major technical problem may arise if silica that is released during the olivine reaction would form a layer on the olivine grains, preventing the reaction to proceed. A possible way out is to mix the olivine sand with some minute quartz grains. Quartz has a much lower solubility than amorphous silica, so the dissolved silica that is released in solution will tend to diffuse to the quartz grains and precipitate as an overgrowth on quartz surfaces instead of on the olivine grains, leaving the olivine surfaces free for continued reaction.

5. Coastal Protection

Olivine can be used in several ways to protect coastlines against erosion. Olivine is considerably heavier than normal quartz sand (specific masses of 3.4 versus 2.65 kg/m3), which makes it more resistant to physical erosion. Olivine blocks can be used in the construction of permeable breakwaters. In a permeable triangular breakwater, pointing into the sea, the force of the longshore (flood and ebb) currents is weakened because part of the water passes through the breakwater and loses momentum in doing so, while another part is deviated from the coast. Both effects reduce coastal erosion. If the sections at either side of the breakwater are covered with olivine sand, it will resist erosion even better.

Another way of using olivine for coastal protection is the construction of olivine reefs at strategic points to keep waves and currents away from the coast. If the seawater that is enclosed in the reefs is only slowly refreshed, its pH will rise as a consequence of the olivine reaction. This may lead to the precipitation of calcite, so that these reefs are self-cementing. They will become hatching and hiding places for fish and a place for mussels and oysters to settle (Figure 6).

Figure 6. The sea as a threat: the Hondsbossche Zeewering along the Dutch Coast.
Stretches of beach that lose sand can be restored by spreading olivine sand on the beaches. Olivine sand on beaches feels well, and children love to build their sand castles with it and make sand sculptures of dolphins and seals (Figure 7).

Figure 7. The sea as an ally. Children making sand sculptures of olivine sand that
will merge with the sea at high tide and help in counteracting ocean acidification.
Very rough coastal stretches can be covered with olivine grit, preferably of various sizes. In imitated surf experiments, we have shown that mixtures of different grain sizes become rounded and are abraded faster than single grain sizes by the multiple grain-to-grain collisions [7]. During this polishing in the surf, small micron-sized slivers of olivine are knocked off (see also Section ‘Olivine in high-energy marine environments’). These slivers react very rapidly with sea water and add alkalinity to counteract ocean acidification. It was even found that brucite (Mg(OH)2) formed already after a few days in experiments with olivine and seawater. From the observations on white smokers [8], it is known that brucite is rapidly transformed into aragonite (Figure 8).

Figure 8. Sixty-meter tall aragonite (replacing brucite) chimneys on Lost City seamount.
Coastal protection with olivine, instead of with the usual basalt blocks, will add alkalinity to the ocean and also provide places of interest to tourists. This makes this combined function of CO2 capture and alkalinity provider also financially attractive. Rough stretches of beach covered with olivine grit can serve as natural tumbling devices, where nicely rounded green grit can be produced by the surf. These may serve for applications as diverse as chicken grit and covering material for driveways. Tourists may also find these polished marbles attractive collector’s items. Using the surf which is free of charge, instead of mechanical crushing and tumbling devices, is an additional modest saving. Another financial advantage is that olivine cargo ships can unload their olivine directly in front of the coast, thus avoiding harbor dues.

6. Olivine in High-Energy Marine Environments

It is a paradigm that weathering on land, and under marine conditions, always would be a slow process. When olivine grains, preferably of different sizes, are free to be kept in motion by currents, their weathering is a fast process. The grains are quickly rounded and abraded by mutual collisions (Figure 9), producing myriads of micron-sized slivers (see picture in Additional file 1; see also [9]).

Figure 9. Angular olivine grains are quickly rounded
and abraded by mutual collisions when kept in motion.
In experiments where modest current action was imitated by letting olivine grains rotate slowly along the bottom of an Erlenmeyer, the water had become opaque white after a few days of rotation, the pH of the solution had gone up, and neoformed grains of brucite, a mineral known to transform into carbonate fast, had evolved.

Many shallow sea floors are covered with gravel. When 700,000 km2 of such sea bottoms are covered each year with a 1-cm thick layer of olivine grit, this would compensate the entire anthropogenic CO2 emissions, and raise the pH of the oceans. To make it more concrete, the following example may serve. Part of the continental shelf between the Shetland Isles and France, i.e. the Southern Bight of the North Sea, the English Channel and the Irish Sea, is covered with sand waves, and in and around the Channel, an area of well over 100,000 km2 experiences bed stresses capable of transporting gravel [10,11]. If a volume of 0.35 km3 coarse olivine is spread over 35,000 km2 of this area, this would compensate 5% of the world’s CO2 emissions, that is more than the combined emissions of the adjoining countries, the UK, France, Ireland, Belgium and the Netherlands together [9].

Another site where the spreading of coarse olivine grit may work out well is the Maelstrom, with very strong tidal current in the Lofoten Islands, Norway, and there are many more suitable areas in shallow shelf seas.

The alkalinity brought in by the olivine is of great importance. It counteracts ocean acidification, and the contained bio-limiting nutrients, Si and Fe, enhance marine productivity thereby capturing additional CO2. Another factor that makes this approach low-cost is that large carriers can bring the olivine directly to the place of use, where they are discharged, thus avoiding harbor dues and additional transport costs.

Results and discussion

A preliminary volume and cost-benefit estimate

At this early stage, it is virtually impossible to provide accurate estimates of the volumes of CO2 involved for each of the options, and of the amount of money potentially won or lost.

Table 1 should, therefore, be taken as a not too-educated guess of the orders of magnitude involved in each of the six options. The large spread in the numbers for the first five options is caused by the uncertainty whether the particular activity will be executed in a few tests on essentially pilot scale, or as a worldwide activity.

Table 1. Estimated order of magnitude of CO2 capture and/or emission reduction and money involved
CO2 capture or emission reduction Cost or benefit  
Unit1 Million ton1 Million euro
1. Nickel farming1 to 500 to +200
2. Biodiesel from diatoms50 to 1,000+10 to +500
3. Quenching forest fires100 to 1,000+200 to + 2,000
4. Supergreen energy20 to 1,000+50 to + 5,000
5. Coastal protection10 to 1,000−1 to + 100
6. Olivine in high-energy waters 25,000−500,0003
3If the figure of 50 billion euro of costs for the option in the last row is compared to the cost of the CCS-option, the deficit changes into a benefit of 0 billion euro [cf. 12].

The cost of the olivine in high-energy shallow seas is calculated as the total costs of spreading 25 Gt of crushed olivine in shallow high-energy seas. When compared to carbon capture and storage (CCS), it should not be marked as a cost of 50 billion euro, but as a benefit of 0 billion euro.


It is likely that the first five examples of large-scale applications of the olivine option that are presented in this paper will all turn out to be profitable or, at least, financially self-supporting without requiring subsidies or carbon credits. The costs/benefits of the spreading of olivine in high-energy shallow seas depend on the way to calculate it. If it is just the cost of the operation itself, this total solution of the climate problem and ocean acidification costs a lot of money (order of 15% of the price of the equivalent amount of crude oil), but if it is compared to the costs of the CCS alternative, which is still on the agenda of several governments, it will save a huge amount of money. The major obstacle may well be that the unusual character of the proposals will delay their introduction because parties have a tendency to shy away from untested innovative approaches. Each of the six represents a major breakthrough in the attempts to control climate change and ocean acidification.


This study utilized stimulation of a chemical reaction that has been common at the Earth’s surface over the last 4.5 billion years.

Competing interests

The authors declare that they have no competing interests.

Authors’ contributions

RDS developed ideas about the use of stimulated olivine weathering as a means to counter human CO2 emissions. PDB carried out flume experiments. Both authors contributed to, read and approved the final manuscript.


Prof. Elburg (Durban) is thanked for suggesting some significant modifications. David Addison from Virgin Group, London is thanked for going through the text and suggesting a number of clearer formulations.

  1. Schuiling RD: Farming nickel from non-ore deposits, combined with CO2 sequestration. Natural Science 2013, 5:4.
  2. Scheffran J, Dürr HH, Wolf-Gladrow DA, De La Rocha CL, Köhler P, Renforth P, Joshua West A, Hartmann J: Enhanced chemical weathering as a geoengineering strategy to reduce atmospheric carbon dioxide, supply nutrients, and mitigate ocean acidification. Rev. Geophysics 2013, 51:113–149.
  3. Schuiling RD, Andrade A: Recovery of struvite from calf manure. Environ. Techn 1999, 20:765–768.
  4. Van der Werf GR, Morton DC, DeFries RC, Olivier JGJ, Kasibhatla PS, Jackson RB, Collatz GJ, Randerson JT: CO2 emissions from forest loss. Nature Geoscience November 2009, 2009:2.
  5. Schuiling RD: Serpentinization as a possible cause of high heat-flow values in and near oceanic ridges. Nature 1964, 201:807–808. no 4921.
  6. Priestnall M: Making money from mineralization of CO2. Carbon Capture Journal, February 03, 2013.
  7. Schuiling RD, de Boer PL: Rolling stones; fast weathering of olivine in shallow seas for cost-effective CO2 capture and mitigation of global warming and ocean acidification. Earth Syst. Dynam. Discuss 2011, 2:551–568. doi:10.5194/esdd-2-551-2011.
  8. Shipboard Scientific Party, Roe KR, Schrenk MO, Olson EJ, Lilley MD, Butterfield DA, Jeff G, Gretchen F-G, Blackman DK, Karson JA, Kelley DS: An off-axis hydrothermal vent field discovered near the Mid-Atlantic Ridge at 30°N. Nature 2001, 412:145–149.
  9. de Boer PL, Schuiling RD: Fast weathering of olivine in high-energy shallow seas for cost-effective CO2 capture as a cheap alternative for CCS, and effective mitigation of ocean acidification. AGU 2013 Fall Meeting, OS13A-1689.
  10. Belderson RH, Wilson RH, Holme NA: Direct observation of longitudinal furrows in gravel, and their transition with sand ribbons of strongly tidal seas. In Tide-Influenced Sedimentary Environments and Facies. Edited by de Boer PL, et al. Dordrecht: Reidel; 1988:79–90.
  11. Mitchell AJ, Ulicny D, Hampson GJ, Allison PA, Gorman GJ, Piggott MD, Wells MR, Pain CC: Modelling tidal current-induced bed shear stress and palaeocirculation in an epicontinental seaway: the Bohemian Cretaceous Basin, Central Europe. Sedimentology 2012, 57:359–388.
  12. McKinsey & Company: Carbon Capture & Storage: Assessing the Economics; Report September 22, 2008.

© 2013 Schuiling and de Boer
This article was published December 21, 2013, at under a Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Friday, December 13, 2013

Ocean Tunnels

Ocean tunnels are proposed by Patrick McNulty as a way to combat global warming. Many of these tunnels, lined up across the Gulf Stream and the Kuroshio Current, could supply large quantities of clean energy to the North American East Coast and to East Asia.

Such tunnels can supply energy continuously, i.e. 24 hours a day, all year, making them suitable to supply base load energy as currently generated by coal-fired power plants and nuclear power plants. 

Ocean tunnels thus hold the potential to supply huge amounts of clean energy and facilitate a rapid move to a sustainable economy, as part of the comprehensive and effective action needed to combat climate change. This is pictured in the image below under part 1. 

Comprehensive and effective action is discussed at the Climate Plan blog

Ocean Tunnels can be combined with Ocean thermal energy conversion (OTEC) methods that use the temperature difference between cooler deeper parts of the ocean and warmer surface waters to run a heat engine to produce energy. Once such a system is in place, it has access to both deeper parts of the ocean and to surface waters, while generating a lot of energy. Such a system can also be used to pull up sunken nutrients from the depth of the ocean and put them out at surface level to fertilize the waters there, while the colder water that is the output of OTEC will float down, taking along newly-grown plankton to the ocean depths before it can revert to CO2, as described in the earlier post Using the Oceans to Remove CO2 from the Atmosphere.

Tunnels could regulate temperatures in the Arctic in a number of ways. The clean electricity they generate can replace ways polluting energy that warms up the Arctic. The clean energy tunnels generate can also be used in projects that help reduce temperatures in the Arctic. Furthermore, the turbines in tunnels can reduce the flow of ocean currents somewhat, thus reducing the flow of warm water into the Arctic.

Additionally, tunnels also hold the potential to divert warm water elsewhere and to move colder water into places that could otherwise get too warm, i.e. part 2. (Heat management) of the above action plan, more specifically management of water temperature.

Tunnels could be shaped to guide the flow of water into a specific direction, which could divert some of the water that is currently going into North Atlantic Current towards the Arctic Ocean down a southwards course along the Canary Current along the coast of West Africa.

Thus, tunnels could both produce energy to pump water elsewhere, or to pump water onto the sea ice and glaciers, to thicken the ice, or to pump sea water up into the air to spray it around and create clouds. The energy could be used in projects to help reduce temperatures in the Arctic. Additionally, tunnels could also be shaped in ways to guide water, which works even when no energy is generated. Tunnels is a concept with many applications and testing and further studies will show which applications are attractive.

A comprehensive action plan will need to consider a wide range of action. A warming Arctic results in changes to the Jet Stream, in turn making that more extreme weather can be expected, as illustrated by the video below, by Paul Beckwith

In July 2013, water off the coast of North America reached 'Record Warmest' temperatures and proceeded to travel to the Arctic Ocean, where it is still warming up the seabed, resulting in huge emissions of methane from the Arctic Ocean's seafloor.
NOAA: part of the Atlantic Ocean off the coast of North America reached record warmest temperatures in July 2013
Diversion of ocean currents could reduce warming of the waters in the Arctic. As the image below shows, warm water is carried by the Gulf Stream all the way into the Arctic Ocean.

Warming up of the waters in the Arctic is threatening to cause release of huge quantities of methane that is held in sediments under the seabed, as discussed in the post Quantifying Arctic Methane.


- Climate change: Solutions to a big problem

- Arctic Methane Release and Rapid Temperature Rise are interlinked

- Causes of high methane levels over Arctic Ocean

- Quantifying Arctic Methane

Wednesday, December 4, 2013

Methane-Eating Microbes Need Trace Metal

Methane can be released from hydrates during an earthquake or by rising ocean temperatures, and this can contribute significantly to global warming. Stimulating microbes to consume the methane in the water could prevent methane from entering the atmosphere and, as a new study has found, trace metals may hold the key. The following is from a Georgia Institute of Technology news release. 

A pair of cooperating microbes on the ocean floor “eats” this methane in a unique way, and a new study provides insights into their surprising nutritional requirements. Learning how these methane-munching organisms make a living in these extreme environments could provide clues about how the deep-sea environment might change in a warming world.
Scientists already understood some details about the basic biochemistry of how these two organisms consume methane, but the details of the process have remained mysterious. The new study revealed that a rare trace metal – tungsten, also used as filaments in light bulbs — could be important in the breakdown of methane.
Glass works in a chamber where she can control the oxygen
levels to mimic the deep sea environment. Credit: Rob Felt.
“This is the first evidence for a microbial tungsten enzyme in low temperature ecosystems,” said Jennifer Glass, an assistant professor in the School of Earth and Atmospheric Sciences at the Georgia Institute of Technology.
The study was recently published online in the journal Environmental Microbiology. The research was sponsored by the Department of Energy, NASA Astrobiology Institute and the National Science Foundation. Glass conducted the research while working as a NASA Astrobiology post-doctoral fellow at the California Institute of Technology, in the laboratory of professor Victoria Orphan.
The methane-eating organisms, which live in symbiosis, consume methane and excrete carbon dioxide.
“Essentially, they are eating it,” Glass said. “They are using some of the methane as a carbon source and most of it as an energy source.”
Phylogenetically speaking, one microbial partner belongs to the Bacteria, and the other is in the Archaea, representing two distinct domains of life. The archaea is named ANME, or anaerobic methanotrophic archaea, and the other is a sulfate-utilizing deltaproteobacteria. Together, the organisms form “beautiful bundles,” Glass said.
For a close-up view of the action on the sea floor, the research team used the underwater submersible robot Jason. The robot is an unmanned, remotely operated vehicle (ROV) and can stay underwater for days at a time. The research expedition in which Glass participated was Jason’s longest continuous underwater trip to date, at four consecutive days underwater.
The carbon dioxide excreted by the microbes reacts with minerals in the water to form calcium carbonate. As the researchers saw through Jason’s cameras, calcium carbonate has formed an exotic landscape on the ocean floor over hundreds of years.
“There are giant mountains on the seafloor of calcium carbonate,” Glass said. “They are gorgeous. It looks like a mountain landscape down there.”
While on the seafloor, Jason’s robotic arm collected samples of sediment. Back in the lab, researchers sequenced the genes and proteins in these samples. The collection of genes constitutes the meta-genome of the sediment, or the genes present in a particular environment, and likewise the proteins constitute a metaproteome. The research team discovered evidence that an enzyme used by microbes to “eat” methane may need tungsten to operate.
The enzyme (formylmethanofuran dehydrogenase) is the last in the pathway of converting methane to carbon dioxide, an essential step for methane oxidation.
Microorganisms in low temperature environments typically use molybdenum, which has similar chemical properties to tungsten but is usually much more available (tungsten is directly below molybdenum on the periodic table). Why these archaea appear to use tungsten is unknown. One guess is that tungsten may be in a form that is easier for the organisms to use in methane seeps, but that question will have to be answered in future experiments.


Methane-Munching Microorganisms Meddle with Metals - Research News, Georgia Institute of Technology

Geochemical, metagenomic and metaproteomic insights into trace metal utilization by methane-oxidizing microbial consortia in sulphidic marine sediments, Jennifer B. Glass et al. (2013)

Tuesday, May 7, 2013

ElectroStatic, NanoCone, Ion Gun, Vortex Separated, Ideal Drop Size, Saltwater Cloud-Cannons

Aaron Franklin
By Aaron Franklin

The apparatus consists of a vertical cylindrical wind-rotor, the interior of which is used as an ideal drop size cloud making machine.
  • The inside surface of the cylindrical wind rotor has metal coated polyester film laminated to it with the metal coated surface facing inwards.
  • The Metal coated Polyester film has been coated with a light sensitive emulsion, photo-exposed in a lattice of dots, and etched to produce an array of nano-cones on the surface of the metal, surounded by a hexagonal lattice of valleys.
  • Spaced by insulators, a few millimeters from the nano-cone surface, is a concentric cylinder of metal mesh. This will probably be silver wire mesh of around 1mm grid spacing and 0.1mm wire gauge.
  • At the centre of the cylinder is a non-rotating, star buttressed spar.
  • The star buttressed spar has microbubble aerated water plumbed through it, to a regularly spaced grid of de-Lavel nozzles, of around 1mm diameter, aiming tangentially at the inside of the rotor, from the outer tips of the star buttress.
  • The water supply aeration is around 50%, with the bubble size controlled to around 0.1mm. This should produce an atomised spray of water droplets around 0.1mm diameter, from the de-Lavel nozzles.
  • The 0.1mm water droplets transfer their energy to rotor rotation, and air vortex motion, in the cylinder of air close to the inner surface of the rotor cylinder.
  • The 0.1mm water droplets pass through the metal mesh, and land on the nanocone surface, producing a thin film of water.
  • A high frequency, high voltage, alternating electric potential is supplied between the nano-cone metal film, and the metal mesh.
  • When the voltage peaks the electric field will cause each Nano-cone to jet a charged micro-droplet of water. The apparatus will be tuned so that these droplets will be around half the ideal size for our perfect clouds.
  • The opposite charge on the metal mesh, will accelerate each charged droplet. The Voltage frequency will be such that the droplet reaches the mesh at the time that the polarity has fully reversed. This will ensure that the droplet passes through the mesh, and is carried by its momentum to the non-rotating airmass at the centre of the rotor.
  • As droplets of alternating polarity are being fired into the rotor-core, each droplet will quickly be attracted to an oppositely charged droplet, combining to form a neutral droplet of the Ideal Size.
  • At the bottom of the rotor cylinder the de Lavels are pointed a little upward to induce a helical input of air-large droplet mixture, entraining and sucking in air from the open bottom of the rotor.
  • The axiswise upward angling of the lower de Lavels reduces the further up the rotor you go, reaching pure tangential before the top. This will create an inwards airflow towards the rotor axis.
At droplet sizes of 8.e-12 litres, 20m rotor 2m diameter = 120sqm of nanocones, nanocone grid spacing 0.2 mm =25 /sqmm= 25 000 000 /sqm = 3 billion, and 5khz electric field....120 litres per second of ideal droplets could be released by this system.
At an average velocity from nanocone to grid of each droplet of 30m/s = 30 000 mm per second... the droplet will travel 3mm in 1/10000 of a second- the time taken for the 5khz field to reverse polarity.  So with these numbers, 3mm gap between the Nanocone surface and the metal mesh seems appropriate.
Tuning will have to allow for evaporative losses from the droplets, however as all the droplets will have the same size and velocity, this should be an easy task.
It may not be necessary at all to use electrostatics. Larger helical angled de Lavels at the bottom of the rotor creating a vortex seperation system where too large droplets impact the inner surface of the rotor, and small enough ones exit at the top may work adequately. A fatter at the bottom, tapered rotor would work well in this case, as it would help expel out the bottom, the waste flow from the too large droplets centrifically.
Star buttresses may not be neccesary on the central spar, particularly with the non-electric version.
Filtering requirements are low, particles smaller than 0.1mm should cause no problems for the electro version, smaller than 1mm no probs at all for the pure vortex model.

Friday, April 5, 2013

Klaus Lackner works on carbon capture technology

Klaus Lackner,
Columbia University
Professor Klaus Lackner, director of the Lenfest Center for Sustainable Energy at the Earth Institute, at Columbia University, is working on technology to scrub carbon dioxide from the air. “Our goal is to take a process that takes 100,000 years and compress it into 30 minutes,” says Lackner.

Direct air capture of carbon dioxide is a method that takes carbon dioxide out of ambient air, as opposed to carbon dioxide that is captured from the point of emissions, say, from the smokestack of a coal-fired power plant.

Lackner and his team are developing a device they call an air extractor, modeled after what is most abundant in nature: the leaf of a tree. There is about 0.5 liter of carbon dioxide in a cubic meter of atmosphere. When the extractor is dry, it loads itself with carbon dioxide from the air; when it's wet it releases carbon dioxide it has captured.

“We can do this at a cost of about $30 a ton of carbon dioxide”, says Lackner, “we have designed a box that can extract about a ton of carbon dioxide a day; it fits into a shipping container”. “If we had 100 million of them", Lackner adds, “we could extract more carbon dioxide out of the air then is currently put in.”

The carbon can be stored in the form of mineral carbonate rock or it can be injected deep in the ground. Alternatively, the carbon dioxide can be used, e.g. by turning it into a fuel. Airplanes will likely need to be powered by fuel for a long time, so captured carbon dioxide could be used to more sustainably produce synthetic jetfuel.

In his lab at Columbia's Engineering School, Lackner has built a small greenhouse, demonstrating that  air extractors loaded with captured carbon dioxide can be placed inside a greenhouse; the humid atmosphere inside the greenhouse will make that the carbon dioxide is released. Adding carbon dioxide to the air inside greenhouses is beneficial for plant growth; the plants will take the carbon dioxide out of the air and use it to grow.


- Prof. Klaus Lackner Takes Step Toward Workable Carbon Capture Technology

- Klaus S. Lackner, Director of the Lenfest Center for Sustainable Energy, Columbia University

- Prof. Klaus Lackner Takes Step Toward Workable Carbon Capture Technolog . .

- Direct Air Capture of Atmospheric Carbon Dioxide

- The Great Debate: CLIMATE CHANGE - Surviving The Future (1:15 to 1:24)

- Funding of Carbon Air Capture

- Removing carbon from air - Discovery Channel

Tuesday, March 5, 2013

Supersonic and high velocity Subsonic Saltwater and Freshwater Cloud Making Cannons

Aaron Franklin
By Aaron Franklin

As a compliment to cloud brightening systems, these for use in calm blue sky conditions, or windy blue sky conditions, over Ocean, sea and glacial ice, and land permafrost.

Also may be very important this year for as high tech cloud brightening/making doesn't look like it will be easy to get out in large unit numbers, while there is existing firepump systems that are available in numbers we need now.

Also are essentially no different from snowmaking gear used on ski fields, except for making snow, lower velocity is fine, and no CCN's are required. Just air below 0C, and freshwater.

- High pressure / high volume fire-fighting/water cannon pump gear can be used as is, or modified for higher pressure and kW capacities to increase output volumes at similar nozzle velocities.

An aerated system looks best at this point because:
  • By using de Laval nozzles ( convergent-divergent, supersonic and tight stream output ) the aerated water can be accelerated by expansion to high velocity or Supersonic speed as it leaves the divergent exit section of the nozzle.
  • Nozzle friction is reduced because air sticks to the surface and creates a gaseous boundary layer.
  • For Aeration, copper or soft stainless tubes CNC laser perforated, swaged to flare to hexagonal ends, stacked for a honeycomb aeration section (just like a ww2 spitfire radiator except they had the water on the outside of the tubes and no holes) fed with compressed air, in the water feed before the pumps can entrain microbubbles in the water. 
  • Alternatively supersonic streams can be achieved with unaerated water with convergent nozzles, but more pressure is required.
  • The high kinetic energy of the water stream will cause excellent dispersion, and evaporation, via transonic shockwaves as the stream slows, shedding its outer layer as it goes, eventually disintegrating completely either below the altitude where enough kinetic energy, has converted to gravitational potential energy for the stream to go transonic if the stream is below a critical diameter, or not far above that altitude if its above that diameter.
  • If its a high velocity Subsonic jet it will still shatter the droplets and evaporate lots of, if not all of them by air turbulence and high differential speed energy conduction/friction evaporation.
  • We need to look at freshwater versions as well. This because saltwater rain will be fine over open oceans but it landing on ice and land permafrost will make them melt faster. And saltwater rain on land living ecologies is not at all good either. There's going to be a big use for them to protect the land permafrosts with cloud cover too. Freshwater versions will benefit from using water with diatoms growing in it, as these act as cloud droplet condensation nuclei, just like salt crystals.

    Seeding tundra lakes with diatoms will also eat CO2, oxygenate the water enhancing aerobic digestion of dissolved methane and other organic carbon. Removing the diatoms with the water for cloud cannons will also remove excess nutrients from the waters, provide aeration for skyborne digestion of DOC to CO2, and will clean up lakes to make them better for winter snow-making watersources.
  • We're going to need to straffe the sky with these things for best cloudmaking effect, so we need to get ready to mount them on naval gun turrets with computer controlled tracking systems and look into parking tanks and APC's with suitable turrets on container ship decks.

    Using these tanks and APC's, maybe fixed installations when the wind is blowing, with cloud-cannons on the arctic tundras can help protect the permafrosts. 

Calculations and conclusions, for peer review:

These are based on a sonic speed case. Faster will give more range but less volume and slower more volume but less range, for a given pump system.

speed of sound 330m/s

Ep= mgh

Ek= 0.5mv^2

Ek sonic (1 kg water)= 0.5 x 1 x 330^2 = 54450J

54450=mgh=1 x 9.8m/s^2 x h

vertical ballistic altitude h=54450/9.8 = 5.556km

cloud water content = 0.3g/m^3

10m thickness= 3g/m^2

100m thickness= 30g/m^2

4 sqkm= 4,000,000 m^2

Fixed position still air straffing:



4 sqkm horizontal Cannon range r = sqrt(4/pi)= 1.12km

Moving ship, land tanker, or wind blowing fixed position straffing:

14m/s = 50km/hr (vehicle or wind velocity)

-4 sqkm per hr requires only 4/50= 80m watercannon range.

Water volume and flow rates:

4sqkm at 10m thick= 12000 liters= 12 tons (less than 10min with flow rates of existing fire pumps)

at 100m thick = 120 tons (could be less than an hour per firepump)

1 small Supersonic cloud cannon could produce 24hr x 4sqkm/hr = 96sqkm of 100m thick cloud per day.

Kinetic energy:

120,000 liters per hr / 3600 = 33.3 L/s

12,000 liters per hr / 3600 = 3.3 L/s

Ek Sonic 1kg = 54.45 kJ

kW 100m thick, 4sqkm cloud layer in an hr = 33.3 L/s x 54.45kJ = 1813 kW

- existing pump designs would need to be upgraded for higher power/pressure to produce this much cloud, if supersonic velocities are required, but this is a very small engineering challenge. Ships trawler size and up, and tanks have more than enough kWs for the job. Rapid small amplitude vertical oscillation of the jet release angle should lay down the average 100m thick cloud bank aimed for.

kW 10m thick, 4sqkm cloud layer in an hr = 3.3 L/s x 54.45kJ = 181.3 kW

- this looks good for mobile straffing with existing fire pumps, provided aerated water and deLavel nozzles are used to produce supersonic velocities. The range required for 4 sqkm per hr coverage at only 80m is no problem for the small volume, aerated supersonic water flows possible from existing fire pumps.

Latent heat of evaporation and Ek sonic considerations:

latent heat of evaporation water = 2260 kJ per L

Ek sonic water = 54.45 kJ per L

  • If the very small water droplets produced by transonic shockwaves shattering any water breaking from the decaying jet should partially or fully evaporate (this will depend on stream velocity) they will be doing this by absorbing a lot of heat from the air they are landing in. This will cool and supersaturate the air with water vapour, and result in rapid droplet condensation in both saltwater and freshwater versions proposed.
  • I am advised that we can expect around 60% humidity levels in arctic conditions. As the evaporative cooling effect will cool the air that the stream droplets land in, and vast quantities of very small cloud nucleation salt crystals will be formed, we can expect a lot more cloud to be formed than the above examples suggest.
  • Aeration should result in more and smaller salt crystals, and droplets. In part due to microbubbles enhancing droplet fragmentation. Also due to supersaturation of the water with air, enhanced by evaporation. This causing many disturbances per drop as new bubbles precipitate, and initiate many salt crystals per droplet to precipitate. Turbulence will also initiate precipitation of air and salt crystals in the supersaturated droplet.
  • How much extra cloud will depend on how much atmosperic turbulence and mixing is generated by the straffing pattern, and on local temperature and humidity conditions.
  • Less mixing will also result in larger cloud droplets.
  • Too much mixing will run the risk of forming little cloud at all, as the humidity levels may be too low to form any droplets at all around the salt crystals.
  • It's quite likely that 500-600kph will be sufficient velocity. This would produce about 15 litres per second from standard firepump gear. A good estimate seems to be that this would initially produce around 100sqkm of 100m thick cloud bank per day. However from what I am hearing there is likely to be a repeating cycle of droplet evaporation - re nucleation of new droplets - back to droplet evaporation, due to the added water vapour and downwind cooling effects. So total cloud produced may be more than this.
  • We should start testing on these ASAP. Others doing testing too, would be a good thing.