Laundry Wastewater Treatment
By Nathan Schiff, PhD
Associate Editor - Institutional
Introduction
Fifty years ago, it seemed OK to discharge untreated wastewater from industrial
processes into rivers and lakes. Many believed that our supply of fresh water
was unlimited and that it could somehow handle the waste. We also weren't
as concerned with the long-term consequences of pollution, neither did we
have the available technology to remedy the situation.
Virtually every Canadian municipality today, has adopted similar by-laws,
specifying what can and can not be discharged into sanitary sewers and the
permissible levels of each contaminant. Pressure from the municipalities
and escalating sewer surcharges, which are applied when contaminant levels
exceed the by-law maximums, are now making it attractive for commercial laundries
to provide their own effective pretreatment program prior to discharging
their wastewater.
What does wastewater from commercial
laundries contain?
Fats, oils and greases (FOG) as well as total suspended solids (TSS), are
the major impurities of concern. These impurities are derived from the soils
which are removed from clothing as well as from the chemicals which are used.
Laundry wastewater may also carry additional impurities, but for the purpose
of this article we will address FOG and TSS, the most common contaminants.
Why are high levels of FOG
so undesirable?
FOG and other organic chemicals are digested, to produce carbon dioxide and
water, by sewage bacteria which feed upon them. In this process, these bacteria
consume and deplete the dissolved oxygen in the water. If untreated wastewater
were to be discharged directly into rivers and streams, it would also deplete
the dissolved oxygen and put marine and plant life risk.
A measure of organic water quality contamination is its Biological Oxygen
Demand or BOD5 . This is a measure of the amount of oxygen wastewater
consumes over 5 days, at 20oC during the biological break down
of organic contaminants, including FOG. The higher the BOD5 level,
the more organic contaminants are present in the water
Most municipalities have set limits of 100-150 ppm for FOG (from vegetable
or animal sources), 350 ppm for TSS and 300 ppm for BOD5. Commercial
laundries which exceed these limits can have surcharges applied to their
water bill; in proportional to the limits exceeded. For laundries using large
volumes of water, this surcharge can be significant, ranging form hundreds
to thousands of dollars per month, and so there is a strong economical motivation
for abiding by the municipal by-laws.
Why are high levels of TSS
undesirable?
Undissolved or insoluble matter, floating or suspended in water, imparts
a cloudy appearance (turbidity) to it, and is referred to as total suspended
solids or TSS.
Aside from its unpleasing esthetic appearance, the main concern with high TSS levels is in its ability to harbor harmful bacteria, such as coliforms. These microorganisms are harmful and can be fatal when ingested. They can readily attach themselves and hide on suspended solids, and are not readily disinfected.
How is Water pretreated before
being discharged?
The topic of wastewater treatment is beyond the scope of this article. Future
articles will address other technologies, including Reverse Osmosis, Ultrafiltration
and Nanofiltration. These are technologies which depend on the size of the
pores in semi-permeable membranes to filter unwanted impurities out of wastewater,
and is carried out under high pressure. A current and very effective new
technology for pre-treating laundry wastewater is through the use of a Dissolved
Air Floatation Unit (DAF Unit).
How and Why Does a DAF Unit
Work?
Recall that a large component of the BOD5 in laundry wastewater
is due to the presence of fats, oils and greases. Reducing the FOG also lowers
the BOD5 level. The economic benefit of using a DAF Unit is in
avoiding a double sewer surcharge; one for excess BOD5 and the
other for a FOG violation
FOG, being lighter than water has a natural tendency to float to the surface
of a wastewater holding tank, from where it can be skimmed off. Since individual
FOG droplets are very small and dispersed throughout a large tank of water,
a considerable amount of time would be required for most of them to reach
and concentrate at the surface. To resolve this problem, the heart of the
DAF Unit consists of a compressed air-in-water tank which works as follows:.
Air is sparingly soluble in water under normal atmospheric pressure. However
compressing air under high pressure, in a water-containing cylinder, results
in a significant amount of the air being physically dissolved. This air enriched
solution is then slowly released from the cylinder into the larger wastewater
holding tank, and millions of tiny air bubbles come out of solution. A similar
phenomena is seen when a soft drink bottle is slowly opened. Hundreds of
gas bubbles are released which either adhere to the walls of the bottle or
float to the surface.
As the tiny air bubbles rise to the surface, they attach themselves to the
dispersed FOG particles, they lift them at an accelerated speed upwards towards
the surface of the tank.
Total suspended solids (TSS), being heavier than water, would tend to sediment,
within time, to the bottom of the holding tank. However, because many of
the tiny air bubbles also surround and attach themselves to each suspended
solid particle, they exert the same lifting effect, to the surface. In so
doing, the turbidity of the solution is reduced, and so is the risk of paying
a 3rd sewer surcharge for violation of TSS maximum levels.
Summary
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