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Selasa, 21 Juni 2011

Iron removal: A world without rules


Iron removal: A world without rules
A compete guide to iron removal methods, equipment & their limitations.
By Scott Harmon

From the April 2003 edition of Water Technology magazine. 

Iron can often be detected visibly in water or by staining on plumbing fixtures.

There is one rule to keep in mind when selecting a method for iron removal — and that is there is no rule. You will find — as with all problem water applications — the solution is 50 percent science and 50 percent experience.

The following information describing the different types of iron removal process applications are the basics. Before using any of these applications, it’s good to have an understanding of the type of iron present; the equipment and its limitations; and the product and processes involved with method.

Equipment

Care must be taken when considering iron removal advice from different regions of the country as water temperature, pH, alkalinity, dissolved oxygen content and other factors will affect the actual results.

Most application failures are caused simply by not selecting the right equipment for the water conditions present. It is important to follow manufacturer’s guidelines regarding flow rates, backwash rates, pH levels, maximum iron input levels, water temperatures and any other application limitations that the manufacturer has noted in order for the equipment and media to deliver their best result as designed.

Water filter 

Most iron filtration systems operate on the principal of oxidizing the iron (oxidation) to convert it from a ferrous (dissolved or soluble) to a ferric or undissolved state. Once in the ferric state, iron can be filtered.

Water filters are the most widely used equipment in removing iron. Its popularity comes from its versatility due to the various media products available and the process involved with each media.

The most common reasons for filter failure are a lack of flow in backwash or a lack of frequency of regenerations. Low pH levels when using filters are another reason for unsatisfactory results.

Water softener

Water softeners exchange ions by design. When used in iron removal, the softener uses a cation resin to exchange iron for sodium, in addition to the calcium and magnesium exchanged for sodium in the softening process.

Softeners are commonly used in removing low levels of ferrous iron (1-3 ppm), though it is not uncommon to remove 10 or more ppm depending on water conditions and control settings.

The last thing a water softener needs is for the ferrous iron to oxidize and convert to a ferric state. Since pH plays a big part in how quickly this conversion takes place, it is important to note that softeners perform better on low pH, which will also prolong bed life.

In the ferric state, iron will coat the resin, plugging the exchange sites and fouling the resin. Iron fouling will eventually happen in any iron application and requires replacement of the media.

High saltings, longer backwashes, frequent regenerations and the use of iron cleaners are keys to longer bed life. However, even after taking these steps to prevent the bed from fouling, the resin will eventually succumb to the iron and require replacement.

Media selection

Each type of treatment has its own strengths and weaknesses. As in the selection of equipment, it is important to follow manufacturers’ recommendations and note any application limitations such as water temperature, pH alkalinity and dissolved oxygen content to get the best result.

To do this, water treatment professionals need a clear understanding of all limitations of the product and equipment selected.

Filtration using various means of oxidation is the most common method of iron removal. Depending on the media selected, other common processes such as ozone, aeration, chlorine or peroxide injection may be used to boost the oxidizing properties of the water being treated.

• Greensand
Greensand is one of the oldest but proven oxidation technologies. Potassium permanganate, itself an oxidizer, is used to regenerate the greensand.

In this application, potassium permanganate produces manganese dioxide on the surface of the mineral and — once the water comes in contact with it — any iron is immediately oxidized. The iron can be filtered and then cleaned away in the backwash cycle. Greensand is also effective with low levels of H2S (hydrogen sulfide) and manganese.

Synthetic greensand is a granular mineral with a manganese dioxide coating having the same ability as regular greensand. It is much lighter and requires less of a backwash rate than standard greensand.

Manganese dioxide
Manganese dioxide is a naturally mined ore with the ability to remove iron, manganese and hydrogen sulfide. The hydrogen sulfide capability exceeds that of either greensand or synthetic greensand and requires no chemicals to regenerate.

It does, however, require adequate amounts of dissolved oxygen in the water as a catalyst and may require some type of pre-oxidation to achieve its maximum ability.

• Birm
Birm has the ability to remove iron and manganese and has no effect on hydrogen sulfide. Like manganese dioxide, birm also uses dissolved oxygen as a catalyst and may require some type of pre-oxidation in cases where the dissolved oxygen content is too low to affect a maximum iron removal result.

• Redox
Redox media, which requires adequate dissolved oxygen to be effective, consists of two metals - 85 percent copper and 15 percent zinc. These two dissimilar metals create a small electrical field in the bed that will not allow bacterial growth in the media.

This property earns redox the unique distinction of being effective on bacterial iron without the use of chlorine injection and being rated as bacterial static.

Effective on removal of iron and hydrogen sulfide, able to reduce chlorine and heavy metals such as lead and mercury, redox is not effective with manganese.

The biggest drawback for this media is its weight. Being almost twice as heavy as other minerals, it requires more than twice the backwash rate of other minerals. Sizing mineral tanks is crucial.

Catalysts & Considerations

Once you have identified the enemy and selected the equipment with compatible backwash and flow rates for the media selected, the water itself must be scrutinized.

Check for dissolved oxygen and pH levels and determine what, if any, pre-treatment is necessary for the selected application to deliver maximum iron removal efficiency.

What is the role of pH?

The pH of a given water source plays an important role in how quickly ferrous (dissolved) iron converts to a ferric (solid) state. The higher the pH, the faster iron will convert to the ferric state that can then be filtered.

This is good in all equipment selections with the exception of a water softener where the ferric iron plugs the exchange sites and fouls the resin.

When using an iron filter a pH above 6.5 is necessary for iron to properly convert and is the recommendation of most manufacturers. However, most experienced water treatment professionals agree that a pH above 7.0 is a must and an 8.0 to 8.5 pH greatly enhances the chance of a successful application.

If it is necessary to increase the pH level, chemical feed of either sodium carbonate (soda ash) or sodium hydroxide (caustic soda) is preferred over a filter filled with calcium carbonate or magnesium oxide, as the filter method may foul quickly.

Pre-oxidation

Most chemical-free iron filters and several chemical filter media require some dissolved oxygen in the water to act as a catalyst. Pre-oxidation is required in cases where the dissolved oxygen content is too low.

Pre-oxidation can come from aeration, chlorine or peroxide injection, ozone and other methods.

Chemical feed

There are several types of chemical feed applications. Using sodium carbonate or sodium hydroxide to raise pH is common. Using 5 percent to 10 percent chlorine or 7 percent hydrogen peroxide as oxidizers to the water before a filter is also widely used.

Different rules apply to each of these methods, from retention or contact tanks to using static mixers. When using different chemicals together, it’s important to understand the compatibility of the chemicals and the safety considerations.

For greater success, follow the manufacturers’ recommendations closely regarding proper feed rates and installation when injecting chemicals.

Aeration

When aeration is used as a pre-oxidizer it is generally done with either an air inductor or an air pump.

An air inductor is a venturi installed inline. The water flowing through the inductor creates a vacuum and sucks air into the water line. The faster the water flows, the more air induced into the water.

Watch for pressure drop and perform routine maintenance of the inductor, as they will clog with iron over time.

The air pump method allows more air induced into the water, as a mechanical pump is used to force air into the water. A contact tank is often used.

This method has proven effective with the only cautions being maintenance to the pump and injection fittings.

Ozone

Ozone is a powerful oxidizer and when used properly can be effective on large amounts of iron. Similar to aeration, ozone is injected into water via a contact vessel as a pre-treatment to filtration.

Ozone generators come in many designs and sizes and a full understanding of the process is necessary for success. Due to ozone’s expense it is usually applied on iron levels higher than normal filtration is known to handle effectively.

Scott Harmon CWS V, CI is manager of technical support for the RainSoft division of Aquion Partners L.P, Elk Grove Village, IL. Harmon started in the water treatment industry as an installer and service technician, and was the service manager for a local RainSoft dealer before joining Aquion as international service trainer.

From the April 2003 edition of Water Technology magazine. 
For a concise description of how the types of iron are identified by the same author, please go here.

Rabu, 20 April 2011

Iron Removal in water


IRON REMOVAL

 

Iron removal is technique used to remove excessive iron and manganese from water. The iron and manganese cause unwanted precipitation and coloring of the water.

Iron removal is based on the controlled precipitation of iron and manganese. It is normally done by mixing of the water with air followed by sand filtration.
Of importance is the pH value of the water. The removal of the iron is normally less difficult than the removal of manganese. High iron concentration should be treated with two or more systems in series.
Complex bound iron and manganese, e.g. complex bound with humic acids, can be very difficult to remove. In this case oxidation with ozone can be a solution.
In order to remove iron, it is also possible to precipitate iron in carbonate or with an iron exchanger system. An ion exchanger system is only used to deal with low Fe 2+ concentration. In addition, ion exchanger resin can remove others cations such as Ca 2+. That is why it is advisable to apply it only with low iron and manganese concentrations


Iron is one of the most abundant metals of the Earth's crust. It occurs naturally in water in soluble form as the ferrous iron (bivalent iron in dissolved form Fe2+ or Fe(OH)+) or complexed form like the ferric iron (trivalent iron: Fe3+ or precipitated as Fe(OH)3). The occurrence of iron in water can also have an industrial origin ; mining, iron and steel industry, metals corrosion, etc.
In general, iron does not present a danger to human health or the environment, but it brings unpleasantness of an aesthetic and organoleptic nature. Indeed, iron gives a rust color to the water, which can stain linen, sanitary facilities or even food industry products. Iron also gives a metallic taste to water, making it unpleasant for consumption. It can also be at the origin of corrosion in drains sewers, due to the development of microorganisms, the ferrobacteries.
In aerated water, the redox potential of the water is such as it allows an oxidation of the ferrous iron in ferric iron which precipitates then in iron hydroxide, Fe(OH)3, thus allowing a natural removal of dissolved iron.

However ground waters are naturally anaerobic: so iron remains in solution and therefore it is important to remove it for a water use.

The elimination of the ferrous iron, by physical-chemical way, is obtained by raising the water redox potential by oxidation thanks to oxygen of the air and this by simple ventilation. In the case of acid water, the treatment could be supplemented by a correction of the pH. Thus, the ferrous iron is oxidized in ferric iron, which precipitates in iron hydroxide, Fe(OH)3. The precipitate is then separated from water by filtration on sand or decantation. The stage of precipitation by chemical oxidation can also be carried out with the stronger oxidants such as the chlorine dioxide (ClO2), ozone (O3) or the potassium permanganate (KMnO4).
This elimination can be carried out by cascade or spraying open-air systems (for an acceptable maximum content of Fe2+ of 7mg.L-1) known as gravitating systems. Those systems require a significant place on the ground, but, in addition to an easy and a cheap exploitation cost, they also make possible aggressive CO2 and hydrogen sulfide (H2S) removal. There are also pressure systems, which in addition to their compactness, make possible to treat water whose Fe2+ concentrations between 7 and 10mg.L-1.
 

Iron is often found in water in complexed forms. In order to be eliminated, iron complexed requests a coagulation stage, which comes in between oxidation and filtration.

Remark : Thanks to microorganisms, it is possible to remove iron from water by biological way. Indeed, there are many bacteria, whose metabolism and thus their survival, are related to the oxidation of iron. However this biological removal requires conditions specific for the pH, the temperature, the redox potential, etc


Advanced Oxidation
Advanced chemical oxidation processes make use of (chemical) oxidants to reduce COD/BOD levels, and to remove both organic and oxidisable inorganic components. The processes can completely oxidise organic materials to carbon dioxide and water, although it is often not necessary to operate the processes to this level of treatment
A wide variety of advanced oxidation processes are available:
  • chemical oxidation processes using hydrogen peroxide, ozone, combined ozone & peroxide,  hypochlorite, Fenton's reagent etc.
  • ultra-violet enhanced oxidation such as UV/ozone, UV/hydrogen peroxide, UV/air
  • wet air oxidation and catalytic wet air oxidation (where air is used as the oxidant)
Advanced oxidation processes are particularly appropriate for effluents containing refractory, toxic or non-biodegradable materials. The processes offer several advantages over biological or physical processes, including:
 - process operability
 - unattended operation
 - the absence of secondary wastes
 - the ability to handle fluctuating flow rates and compositions


CWAO process
However, advanced oxidation processes often have higher capital and operating costs compared with biological treatment.
The most suitable variant for each application is chosen on the basis of the chemical properties of the effluent.


Manganese Removal by physical-chemical way


As for iron, the origin of manganese, in water, is at the same time natural (dissolution of the reduced form Mn2+) and industrial (mining, the iron and steel industry, etc). The same goes for its removal from water. Manganese does not present a danger to human health, nor for the environment but it is unpleasant. In fact, the water gets a black color and a metallic taste.

Similar to iron, the manganese removal by physical-chemical way, can be carried out by the oxidation of Mn2+ in Mn4+, which precipitates then in manganese dioxide (MnO2). The precipitation is then separated from water by filtration on sand or decantation.
The only difference (with the iron), is in the reagent used. Indeed, oxidation by oxygen is in many cases not sufficient for manganese, which implies the use of stronger oxidants in complement such as dioxide of chlorine (ClO2), chlorine (Cl2), potassium permanganate (KMnO4) or ozone (O3).



Remark : In the same way for iron, manganese can be removed by biological way. There are bacteria which take their energy from the oxidation of manganese and which require a water with specific conditions to have an optimal activity of the micro-organisms. However, even if it is possible to carry out in the same time the iron and manganese removal by physical-chemical treatment, the same doesn’t go for the biological way. In fact, the iron and the manganese specific bacteria need different environmental conditions.