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Sunday, December 25, 2016

GROUNDWATER DEPLETION AND SALT WATER INTRUSION - One water-quality threat to fresh groundwater supplies is contamination from saltwater intrusion.



Groundwater depletion, deterioration of water quality and saltwater intrusion
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Groundwater depletion
Groundwater is a valuable resource throughout the world. Where surface water, such as lakes and rivers, are scarce or inaccessible, groundwater supplies many of the hydrologic needs of people everywhere.
In the United States, it is the source of drinking water for about half the total population and nearly all of the rural population. it provides over 50 billion gallons per day for agricultural needs.
Groundwater depletion, a term often defined as long-term water-level declines caused by sustained groundwater pumping, is a key issue associated with groundwater use.
Excessive pumping can overdraw the groundwater "bank account"
The water stored in the ground can be compared to money kept in a bank account. If you withdraw money at a faster rate than you deposit new money you will eventually start having account-supply problems.
Pumping water out of the ground faster than it is replenished over the long-term causes similar problems. The volume of groundwater in storage is decreasing in many areas as a result of over pumping. 
Groundwater depletion is primarily caused by sustained groundwater pumping.
What are some effects of groundwater depletion?
Pumping groundwater at a faster rate than it can be recharged can have some negative effects of the environment and the people who make use of the water:
Some of the negative effects of groundwater depletion are:
·      drying up of wells
·      reduction of water in streams and lakes
·      deterioration of water quality
·      increased pumping costs
·      land subsidence

Lowering of the water table

The most severe consequence of excessive groundwater pumping is that the water table, below which the ground is saturated with water, can be lowered. For water to be withdrawn from the ground, water must be pumped from a well that reaches below the water table.
If groundwater levels decline too far, then the well owner might have to deepen the well, drill a new well, or, at least, attempt to lower the pump. Also, as water levels decline, the rate of water the well can yield may decline.

Increased costs for the user

As the depth to water increases, the water must be lifted higher to reach the land surface. If pumps are used to lift the water (as opposed to artesian wells), more energy is required to drive the pump. Using the well can become prohibitively expensive.

Reduction of water in streams and lakes

There is more of an interaction between the water in lakes and rivers and groundwater than most people think. Some, and often a great deal, of the water flowing in rivers comes from seepage of groundwater into the streambed.
Groundwater contributes to streams in most physiographic and climatic settings. The proportion of stream water that comes from groundwater inflow varies according to a region's geography, geology, and climate.
Groundwater pumping can alter how water moves between an aquifer and a stream, lake, or wetland by either intercepting groundwater flow that discharges into the surface-water body under natural conditions, or by increasing the rate of water movement from the surface-water body into an aquifer.
A related effect of groundwater pumping is the lowering of groundwater levels below the depth that streamside or wetland vegetation needs to survive. The overall effect is a loss of riparian vegetation and wildlife habitat.

Land subsidence

The basic cause of land subsidence is a loss of support below ground.
In other words, sometimes when water is taken out of the soil, the soil collapses, compacts, and drops. This depends on a number of factors, such as the type of soil and rock below the surface.
Land subsidence is most often caused by human activities, mainly from the removal of subsurface water.

Deterioration of water quality - saltwater intrusion

One water-quality threat to fresh groundwater supplies is contamination from saltwater intrusion.
All of the water in the ground is not fresh water; much of the very deep groundwater and water below oceans is saline.
In fact, an estimated 3.1 million cubic miles (12.9 cubic kilometers) of saline groundwater exists compared to about 2.6 million cubic miles (10.5 million cubic kilometers) of fresh groundwater .
Under natural conditions the boundary between the freshwater and saltwater tends to be relatively stable, but pumping can cause saltwater to migrate inland and upward, resulting in saltwater contamination of the water supply.
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source: water.usgs.gov

Saturday, December 24, 2016

Chlorine Taste In Your Drinking Water - Chlorine produces BACTERIA-FREE WATER, and eliminates algae and slime. It also removes hydrogen sulfide from ground water (wells, springs), and eliminates iron bacteria (cenothrix) which are associated with objectionable odor and taste.

Chlorine Taste In Your Drinking Water?
"If you can smell or taste Chlorine in your drinking water - THERE ISN'T ENOUGH CHLORINE RESIDUAL IN IT!"
Chlorine produces BACTERIA-FREE WATER, and eliminates algae and slime. It also removes hydrogen sulfide from ground water (wells, springs), and eliminates iron bacteria (cenothrix) which are associated with objectionable odor and taste.
Despite these important facts, some people STILL object to Chlorine in their drinking water. Comments like "I don't like the way Chlorine makes my water taste" are common.
THE BAD TASTE IS ACTUALLY DUE TO AN INSUFFICIENT RESIDUAL OR THE LACK OF CHLORINE IN THEIR WATER.
The proper dosage of Chlorine, to maintain the required minimum residual of "FREE" Chlorine is the important key.
If the residual falls below the "FREE" minimum, the reforming of chlororganics and chloramines (the taste and odor producing part of the disinfection process) takes place as a result of increased contamination (Chlorine Demand).
The increased levels can be a result of a main break, cross connection, increased bacteria growth from a dead-end line, or a combination of all of these, and more.
There are some who favor switching to bottled water to avoid drinking chlorinated water.
Consumers may be startled to learn that some brands of bottled water contain CANCER-CAUSING CHEMICALS in amounts that EXCEED FEDERAL STANDARDS. If these chemicals are found in bottled water, there are NO regulations that require the PUBLIC TO BE NOTIFIED!
The Kansas Department of Health and Environment conducted a study of 80 bottled water samples, which were collected from retail stores and manufacturers between March 21 and May 22, 1994.
In 15% of the bottled water, cancer-causing chemicals were discovered. Nine (9) contaminants were found in amounts that
exceed federal limits. The results weren't made public until 14 MONTHS LATER.
When the same type of tests are given to a municipal or rural water district, producing potable drinking water, the public must be informed IMMEDIATELY of any contaminants found in excess of EPA limits.
The water district would then be tested on a more frequent basis. The customers in the affected district are encouraged to drink bottled water, but the bottled water could also be contaminated.
Many brands of bottled water begin as TAP WATER from public water system, with the chlorine residual removed! After this, the bottled water is given a two year shelf life, or more. There are little or no restrictions in the environment in which the water is stored.
The complete elimination of deadly diseases such as cholera, typhoid and others is now taken for granted, thanks to the effectiveness of CHLORINATED WATER.
So why would anyone chance the return of a disease like this, or chance deaths from E-coli or other contamination. Many say "We will wait to disinfect when we are told we have to".
The recent deaths in the City of Walkerton, Ontario, June 2000, were caused by E-coli, as a result of run-off from cattle. WHAT GOES IN THE GROUND TODAY, YOU WILL DRINK TOMORROW. This is reason enough to chlorinate properly.
Chlorine has been available since the early 1900's, and has overwhelmingly proved its effectiveness since that time.
Chlorine is as important to pure water as the polio vaccine has been to children and adults' health. Both continue to keep disease away from humans. Polio vaccination is mandatory for our school children.
Anti chlorine in the drinking water is mandatory in MOST states. In the remaining states, it would seem very important to consider the benefits, cost effectiveness, and the safety record of chlorine gas (the purest form of chlorine) when fed through an all vacuum mounted chlorinator such as REGAL.
Tachmina Solenoid-Driven Metering Pump
This machine regulates the dosing 
of Sodium Hypochlorite into the 
system without need for human intervention.
Water quality can be obtained by many forms of processes and alternative means of disinfection. However, a minimum residual level of the disinfectant has to be provided at the furthest distance from the injection point.
Chlorine, so far, is the only disinfectant approved that provides this required measurable residual amount. Clean, efficient, pure, 100% Chlorine is only available in gaseous form and it has the safest accident record as a bonus.
Calcium Hypochlorite, at 65% and Sodium Hvpochlorite, containing 10-15% available chlorine are PERCEIVED to be safer. However, their easy-to-use containers allow for accidents and could possibly allow contamination even during the manufacturing process.
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For technical information about Chlorination for Paste and odor control; water main sterilization; algae and slime control.- Hydrogen Sulphide removal ; Iron and Manganese; cooling towers.- low pressure drip irrigation systems; poultry drinking/processing water; and dechlorinating - Contact: Chlorinators Incorporated, 1044 SE Dixie Cutoff Road
Stuart, FL 34994, Phone: (561) 288- 4854,
Fax: (561) 287-3238, www. regalchlorinators. Com
E-mail: chlorinc@aol. com
http://www.wateronline.com/doc/chlorine-taste-in-your-drinking-water-0001

Monday, December 12, 2016

POULTRY WATER QUALITY - Water is the most important nutrient for poultry. In addition to being a nutrient, water also softens food and carries it through the body, aids in digestion and absorption, and cools the body as it evaporates through the bird’s lungs and air sacs. Under normal conditions, chickens will consume, by weight, approximately twice as much water as food.

POULTRY WATER QUALITY
A.  Introduction
Water is the most important nutrient for poultry. In addition to being a nutrient, water also softens food and carries it through the body, aids in digestion and absorption, and cools the body as it evaporates through the bird’s lungs and air sacs.
Water helps remove waste, lubricates joints, is a major component of blood, and a necessary medium for many chemical reactions that help form meat and eggs.
Although water is regarded as the most essential nutrient, it is impossible to state its exact requirement. Under normal conditions, chickens will consume, by weight, approximately twice as much water as food.
During periods of extreme heat stress, water requirements may easily quadruple.
Table 12.1 indicates the typical quantities of water required for various poultry species and age.
  Table 12.1 - Approximate water consumption for poultry (gallons/100 birds/day)

Type of
poultry

Normal ambient temperature
(68°F/20°C)
Hot weather (89.6°F/32°C)
Average (growing)

Mature birds

Mature birds
Layer pullets
2.64
3.43
5.28
Breeder pullets
3.17
4.23
6.60
Layer hens
-----
5.55
10.57
Broiler breeders
-----
7.93
15.85
Broiler chickens
4.23
6.60
13.21
Roaster chickens
5.28
7.93
15.85
Broiler turkey
7.66
14.27
26.42
Heavy female turkeys
10.04
16.91
31.70
Heavy male turkeys
14.53
26.42
47.55
Adequacy of a water supply is typically evaluated in terms of how many gallons per minute (gpm) it can deliver on a sustained basis.
A typical 500-ft broiler house requires about 2 gpm for drinking water, so a 5-house complex would require a 20-gpm water supply, just for drinking water for the broilers.
For comparison, a well for a single-family residence is usually judged to be adequate if it can deliver around 4-5 gpm.
Evaporative cooling systems, using either foggers or pads, typically require about 8 gpm per house, which will up the total water requirement per house to 10 gpm.
Recirculating pad systems are more efficient in water use than non-recirculating types, in that water not evaporated is ‘recycled’ and not lost.
However, with either type system, almost all the water will be evaporated into the air going into the house during peak hot weather demand times, so the design gpm requirement will be the same no matter which type evaporative cooling system is used.
B. Evaluating water quality
When water looks clear and tastes okay, water quality is easy to take for granted. However, water quality is impossible to judge adequately except with laboratory testing.
Field experience has conclusively shown that unobservable differences in water quality, from farm to farm and even from one well to another within a complex, can result in significant differences in bird performance.
Drinking water should be clear, tasteless, odorless, and colorless. As a general observation, a reddish-brown color may indicate the presence of iron, while a blue color indicates the presence of copper.
Hydrogen sulfide is indicated by a rotten egg odor. Hydrogen sulfide may also combine with iron to form black water (iron sulfide) that may also implicate the presence of sulfate-reducing bacteria.
Taste can be affected by the presence of salts, and a bitter taste is usually associated with the presence of ferrous and manganese sulfates.
Water quality attributes can have a direct or indirect effect on performance. Poor water quality can retard growth, curtail egg production, or produce lower egg quality.
Feed conversion, for example, has been positively correlated to the presence of sulfate and copper concentrates in the water, and livability with potassium, chloride, and calcium.
Body weight is positively influenced by water hardness and dissolved oxygen and negatively influenced by total bacteria and a pH less than 6.0.
While several elements can cause poor water quality, the interaction between elements is more significant in water quality problems than the simple fact of their presence.
Table 12.2 lists the standards for water quality for poultry use.
Table 12.2 - Drinking water quality guidelines for poultry.
Contaminant or characteristic
Level considered average
Maximum acceptable level
Remarks
Bacteria
Total bacteria
Coliform bacteria

0/ml
0/ml

100/ml
50/ml

0/ml is desirable
0/ml is desirable
Nitrogen compounds
Nitrate
Nitrite

10 mg/l
0.4 mg/l

25 to 45 mg/l
4 mg/l

Levels from 3 to 20 mg/l affect performance.
pH
6.8 to 7.5
----
A pH of less than 6.0 is not desirable. Levels below 6.3 may degrade performance.
Total hardness
60 to 180
----
Hardness levels < 60 are unusually soft; those > 180 are very hard.
Naturally occurring chemicals
Calcium
Chloride

60 mg/l
14 mg/l

----
250 mg/l
Levels as low as 14 mg/l may be detrimental if the sodium level is higher than 50 mg/l.
Copper
0.002 mg/l
0.6 mg/l
Higher levels produce a bad odor and taste.
Iron
0.2 mg/l
0.3 mg/l
Higher levels produce a bad odor and taste.
Lead
----
02 mg/l
Higher levels are toxic.
Magnesium
14 mg/l
125 mg/l
Higher levels have a laxative effect. Levels > 50 mg/ml may affect performance if magnesium and chloride levels are high.
Sodium
32 mg/l
----
Levels above 50 mg/l may affect performance if the sulfate or chloride level is high.
Sulfate
125 mg/l
250 mg/l
Higher levels have a laxative effect. Levels >50 mg/l may affect performance if magnesium and chloride levels are high.
Zinc
----
1.50 mg/l
Higher levels are toxic.
Source: Adapted from T.A. Carter and R.E. Sneed, Drinking water guidelines for poultry. Poultry Science and Technology Guide No. 42, North Carolina State University
Bacteria
The presence of microorganisms is typically a result of surface contamination by organic minerals and can result in poor performance.
The presence of coliform bacteria is generally related to fecal contamination of drinking water due to runoff to surface or ground waters.
Ideally, bacterial contaminants should not be present in drinking water and measurable levels should be zero. The first step towards eliminating contamination is to determine if the source is the well or the distribution system.
Samples taken for bacterial testing should be obtained in a sterile manner and may need to be taken at the source and at strategic points to localize any problems.
Chlorination or filtration of the water supply can eliminate bacterial contaminants. For a properly sealed and located well, treatment of the well cavity with a chlorine source such as sodium hypochlorite may remedy the problems.
If continuous chlorination seems necessary, it should be applied gradually. Between two and five ppm of residual chlorine is recommended.
Start at the lower concentration and increase it until control is satisfactory. Since water intake is the most sensitive criteria, it should be monitored during this process for signs of intolerance.
Long term correction may require well sealing or re-siting. Chlorine levels in the water can also be monitored using a pool test kit.
A common water quality problem in the Southeast U.S. is excess iron, along with bacteria that feed on the iron and form a reddish brown slime that clogs filters, drinkers and fogger nozzles.
Mild iron bacteria problems can often be dealt with by ‘shock chlorination,’ which involves a one-time treatment between flocks, injecting a strong chlorine solution into the well and circulating and flushing it through all pipes in the system.
For more severe iron bacteria problems, continuous chlorination is called for, installing a ‘chlorinator’ to continuously inject chlorine into the water system.
Chlorine not only kills bacteria but is an oxidizing agent, meaning it causes minerals such as iron and manganese to combine with oxygen, in the process coming out of solution and forming a solid precipitant.
Because of this reaction, a sand media filter must be installed downstream from the chlorinator to remove the mineral solids from the water.
Chlorination also prevents other kinds of bacterial contamination, and may be needed even if iron and iron bacteria are not present in the water supply.
Use of an iodine-base disinfectant to control bacteria in drinking water is effective and provides more residual activity but is usually more expensive than chlorination.
Be sure to use only approved chemicals at the recommended rates and ensure that the chemicals are compatible with watering equipment.
Also, be sure to remove the disinfectant from the waterers and water lines before using a water vaccine or medication that is incompatible with the disinfectant.
12.5 Nitrogen compounds
Nitrates (NO3) are produced during the final stage of decomposition of organic matter. Their presence in water usually indicates contamination by runoff containing fertilizer or human and animal wastes.
Nitrates are soluble and may move with surface runoff or leach into the groundwater by percolation through the soil. Nitrates from sources such as animal and human wastes, nitrogen fertilizer, crop residues, and industrial wastes may move considerable distances in the ground.
Nitrite (NO2) is produced during intermediate stages of the decomposition of organic compounds.
The toxicity of nitrates to poultry varies with the age of the birds, older birds being more tolerant.
Research with commercial broilers have shown that nitrate levels greater than 20 mg/l have a negative affect on weight, feed conversion, or performance.
Levels between 3 and 20 mg/l are suspected to affect performance.
Nitrites are toxic at much lower levels than nitrates; concentrations as low as 1 mg/l can be toxic.
Nitrate itself is not toxic. After ingestion, however, it is converted to the toxic form of nitrite by microorganisms found in the intestinal tract of the bird.
Once absorbed into the bloodstream, nitrite binds strongly to hemoglobin and, thereby, reduces the oxygen carrying capacity of the blood.
Chronic nitrate toxicity causes poor growth, anorexia, and poor coordination. Students demonstrate that nitrate nitrogen levels in the drinking water as low as 3 to 5 mg/l depress broiler growth rate.
Well-drilling techniques have improved since many of the older, shallow wells were constructed. If nitrate or nitrite levels in your well water are too high and you cannot eliminate the source of contamination, drilling a new or deeper, properly constructed well may solve the problem.
Nitrate is a very soluble substance, easily dissolved in water and extremely hard to remove. Treatment for nitrate is, therefore, very complicated and expensive.
The three methods of reducing or removing nitrate are:
• Demineralization by distillation or reverse osmosis
• Ion exchange
• Blending
Demineralization removes nitrate and all other minerals from the water.
Distillation is one of the oldest, most effective types of demineralization.
The distilling process has only three steps:
1. The water is boiled;
2. The resulting steam is caught; and
3. The steam is condensed on a cold surface, turning back into water. The nitrate and other minerals remain concentrated in the boiling tank.
Reverse osmosis is another way to de-mineralize water. It reduces but does not remove all nitrates.
In a reverse osmosis system, the water is put under pressure and forced through a membrane that filters out minerals and nitrate. One-half to two-thirds of 12.6 the water remains behind the membrane as rejected water.
The yield of treated water to reject water is related to the amount of pressure applied; the lower the water pressure, the greater the volume of reject water.
Higher-yield systems use water pressures in excess of 150 psi. The systems that operate using standard household water pressure (35 to 45 psi) will yield some treated water, but a large amount of untreated water goes down the drain, and could reduce the efficiency of home septic systems.
Household units are usually small enough to fit under the sink or on a kitchen counter. Both of these demineralization systems require a lot of energy to operate efficiently and are high-maintenance systems. They are also low-yield systems that may provide enough water for a family, but cannot produce the large quantities needed for livestock.
The second type of water treatment for nitrate contamination is ion exchange.
Ion exchange introduces another substance that trades places with the nitrate. Most often chloride is exchanged for nitrate.
The ion exchange unit is a tank filled with special resin beads that are charged with chloride. As water containing nitrate flows through the tank, the resin takes up nitrate in exchange for chloride.
In time, all the chloride will be exchanged for nitrate. The resin can then be recharged by back washing with a brine solution (sodium chloride) and reused.
Because ion exchange systems can treat large volumes of water, they are more appropriate than demineralization for treatment of livestock water supplies.
There are, however, some drawbacks to ion exchange systems.
- First, in addition to exchanging nitrate, the resin beads will also take up sulfate in exchange for chloride. Therefore, if sulfates are present in the water supply, the capacity of the resin to take up nitrate is reduced.
- Second, the resin may also make the water corrosive. For this reason, the water must go through a neutralizing system after going through the ion exchange unit.
- Finally, backwash brines, which are high in nitrate, must be disposed of properly so they do not re-contaminate the groundwater supply.
The third and most common way to reduce nitrates is to dilute the nitrate-polluted water by blending it with water from another source that has low nitrate concentrations. Blending the two waters produces water that is low in nitrate concentration. Blended water is not safe for infants but is frequently used for livestock.
There is no simple way to remove all nitrates from your water. Although it is common to think of boiling, softening or filtration as a means of purifying water, none of these methods reduce nitrate contamination.
Boiling water is, in fact, the worst thing to do because it actually concentrates the nitrate.
Softening and filtration do nothing at all to remove nitrate.
pH - The acidity or alkalinity of water is measured by pH.
A pH of 7 indicates that the water is neutral, a pH less than 7 indicates acidity, and a pH greater than 7 indicates alkalinity.
Low pH water can be unpalatable, corrosive to equipment, and may have a negative impact on performance.
High pH water is also unacceptable since it reflects high levels of calcium and magnesium, which can clog watering systems.
Poultry accept water on the acid side better than they accept water on the alkaline side.
12.7 Hardness
Hardness refers to the presence of dissolved minerals such as calcium and magnesium in either bicarbonate or sulfate form and is expressed as an equivalent of calcium carbonate. It measures the tendency of water to precipitate soap and form scale.
Hard water is commonly associated with the buildup of deposits and the formation of scale in the components of the watering system. Hardness is not commonly harmful to poultry unless certain ions are present in toxic amounts.
High levels of magnesium sulfate (MgSO4) may cause an increase in water consumption, wet droppings, and a drop in production.
Iron, aluminum, and zinc can also contribute to hardness and should be considered if present in unusual amounts.
Extreme hardness may diminish the effectiveness of water-administered medications, disinfectants, and cleaning agents. Hardness should not be confused with salinity.
Water can be very soft with low levels of calcium and magnesium, yet have a high salinity value from dissolved sodium salts. Most ground waters have hardness values of less than 2000 mg/l (may be higher in arid areas).
Occasionally, hardness is reported as grains per gallon (1 grain per gallon is equivalent to 17.1 mg/l).
Water hardness has been classified as follows:
      Hardness range (mg/l)
Description:    0 – 60  Soft
                 61 – 120  Moderately hard
               121 – 180  Hard
                    > 180 - Very hard
When hard water is a problem in proper equipment operation, it can easily be ‘softened’ with commercial water treatment equipment.
Most of the processes exchange the sodium ion from sodium chloride for other minerals present.
It is recommended that the sodium of softened water be monitored because it may influence the amounts of fish meal, defluorinated phosphate, bakery products or salt used by your nutritionist.
Salinity
Salinity refers to salts dissolved in water.
The anions (negatively charged ions) commonly present include: carbonate, bicarbonate, sulfate, nitrate, chloride, phosphate, and fluoride.
The cations (positively charged ions) include calcium, magnesium, sodium and potassium.
Salinity may be measured as Total Dissolved Solids (TDS) or Total Soluble Salts (TSS) and is expressed as parts per million (ppm) which is equivalent to milligrams per liter (mg/l) or micrograms per milliliters (μg/ml).
Salinity may also be measured by electrical conductivity and is then expressed as reciprocal micro ohms per centimeter (omhos/cm) or decisiemens per meter (dS/m).
Salinity by itself tells nothing about which elements are present, but this may be of critical importance. So when the salinity is elevated, the water should be analyzed for the specific anions.
Total Dissolved Solids
Measurement of total dissolved solids (TDS), or salinity, indicates levels of inorganic ions dissolved in water. Calcium, magnesium, and sodium salts are the primary components that contribute to TDS.
High levels of TDS are the most commonly found contaminants responsible for causing harmful effects in poultry production.
Table 12.3 provides guidelines suggested by the National Research Council for the suitability for poultry water with different concentrations of total dissolved solids, which are the total concentration of all dissolved elements in the water.
Table 12.3 - Suitability of water with different concentrations of Total Dissolved Solids (TDS)
TDS (ppm)
Comments
Less than 1,000
These waters should present no serious burden to any class of poultry.
1,000 to 2,999
These waters should be satisfactory for all classes of poultry. They may cause watery droppings (especially at higher levels) but should not affect health or performance.
3,000 to 4,999
These are poor waters for poultry, often causing watery droppings, increased mortality, and decreased growth.
5,000 to 6,999
These are not acceptable waters for poultry and almost always cause some type of problem, especially at the upper limits, where decreased growth and production or increased mortality probably will occur.
7,000 to 10,000
These waters are unfit for poultry but may be suitable for other livestock.
More than 10,000
These waters should NOT be used for any livestock or poultry.
Source: National Research Council. 1974. Nutrients and toxic substances in water for livestock and poultry. National Academy of Sciences, Washington, DC
Mineral contaminants
A wide variety of minerals are commonly found in drinking water. Normally, they are found in relatively low concentrations and cause no harm (see Table 12.2).
High concentrates of sulfates can combine with magnesium to form Epsom salt or with sodium salts that cause a laxative effect and can result in wet litter.
High concentrations of sodium or chloride may also increase water consumption and increase litter moisture.
High levels of sulfate may also interfere with the intestinal absorption of other minerals such as copper.
High levels of magnesium are only a problem in the presence of high sulfate levels since they combine to form Epsom salt.
The formation of scale in the watering system can be attributed to high levels of or combinations of sulfate, magnesium, or calcium. 12.9
High levels of iron may encourage the growth of bacteria, which can lead to diarrhea. When the ferrous form of iron present in well water is exposed to the air, it is converted to the ferric hydroxide form commonly referred to as rusty water.
Other contaminants in the water may include pesticides, herbicides, industrial residues, petroleum products, and heavy metals such as lead or cadmium. Such contaminants are more difficult to detect and require more costly testing procedures.
Turbidity
Turbidity results from the suspension of materials such as silt, clay, algae or organic materials in water.
Levels of turbidity above 5 ppm result in unpalatable water and indicate surface contamination.
Turbid water can be filtered to remove particular contaminants and prevent clogged water lines.
C. Water management
• Conduct water tests. Each farm should have its well water tested. Water quality can change during periods of heavy rain or drought, and additional water tests during these periods will ensure that water lines continue to deliver adequate water volume for both the birds and the cooling systems.
• Change filters regularly. Sediment and other particulates can cause leaky water nipples that can have negative effects on litter quality. Clogged filters restrict water flow to the drinker and cooling systems.
In some cases, simple cartridge filters may not be adequate, such as for water with high iron. In those cases, consider other water treatments.
• Flush water lines regularly. Perform a high pressure flush on water lines between each flock and after adding supplements through the medicator (i.e., vaccine, medications, vitamins, electrolytes, etc.).
• Plan ahead before treating water. Before implementing water treatment or sanitation programs, consult your county agent to be sure contaminants in your water will not react negatively and cause the water system to become clogged.
D. Water treatments
Various methods are available that can reduce or eliminate the impurities that adversely affect water quality.
Chlorination
Chlorination is the most common method used to treat water for bacterial contamination and effectively eliminate bacteria from the water supply.
Chlorine can be administered through an in-line proportioner. General recommendations are to have a level of 2 or 3 12.10 ppm at the drinker farthest from the proportioner.
Chlorine levels can be easily monitored using a pool test kit.
Softeners
Use water softening equipment to reduce hardness. Most softening equipment uses ion exchange to effectively remove the calcium and magnesium ions and replace them with sodium ions.
Levels of TDS, however, are simply substituted and increases in sodium concentration of the water occur, possibly to unacceptable levels.
Poultry are generally sensitive to increases in sodium levels, so producers should be judicial in their selection and use of water softening equipment.
Polyphosphates
Polyphosphates are chemical compounds used primarily to prevent the buildup of scale in the watering systems. They act to cause mineral contaminants to go into solution more readily.
Electrical/Magnetic devices
Electrical or magnetic devices keep minerals associated with scale buildup in solution by altering their electrical charges.
E. Water temperature
Drinking water temperatures should be between 50°F to 60°F (10°C to 15°C) for the most comfortable consumption by mature birds, but some studies have indicated that water temperatures of about 77°F (25°C) reduce mortality in chicks and poults.
Temperatures over 86°F (30°C) will reduce consumption and birds will refuse to drink if water temperatures are over 111°F (44°C).
Guidelines for chlorination
• Do not chlorinate market age birds under extreme heat stress.
• Measure residual chlorine at the waterer to maintain at least a 1.0 ppm level at the drinker mid-house.
• Discontinue chlorination and administer powdered milk solution before vaccination to neutralize chlorine since chlorine kills vaccines.
• Use caution since chlorine solutions are acidic


PURICARE 
INDUSTRIAL 
ENTERPRISES 
Water 
Treatment 
Systems




http://puricare.blogspot.com/p/company-profile.html
Ballast-Type
Pressure Tanks



source: freedrinkingwater.com
Houston Water Pump with
Mazaki Automatic Pump Controller
http://www2.ca.uky.edu/poultryprofitability/Production_manual/Chapter12_Water_quality/Chapter12.pdf