TREATMENT OF PERCOLATE FROM DUMPING SITE
The
percolate is the fouled liquid sewage that forms, in an anaerobic environment,
in a dumping site producing methane, carbon dioxide, high boiling organics (COD
surface active agents, oils, greases. etc), low boiling organics (free acids,
etc), ammonia, anions (chlorides, sulfides, etc), cations (metals, sodium, etc),
suspended and settling material.
|
Due to the large possibility of very large types of composition, as
you can see from the side table, is compulsory to proceed with an analysis
before of the elaboration of the offer, just to characterize the type and
composition of the liquid. |
pH |
5,0 ÷
8,8 |
|
COD, mg/l |
500 ÷
30.000 |
|
|
BOD5,
mg/l |
50 ÷
17.000 |
|
|
NTK, mg/l |
20 ÷
6.000 |
|
|
Metals, mg/l |
5 ÷
500 |
|
|
Chlorides, mg/l |
800 ÷
5.000 |
|
|
Sulfides mg/l |
600 ÷
4000 |
|
|
Nitrates, mg/l |
50 ÷
800 |
The
treatment of a percolate from a dumping site can be briefly described as follows:
1. Extraction,
accumulation and settling;
2. Pretreatment:
pH correction and incondensable elimination;
3. Multi effects
vacuum evaporation;
4. Finishing on
osmotic membranes;
5. Treatment on
activated carbon;
6. Stocking of
the final treated liquid;
|
1) Extraction, accumulation and settling The meteoric waters that are percolating trough the material of a
dumping site are collected, periodically, by a pumping station from the sump
pits and stored in covered pools or storage tanks. This liquid accumulation allows the settling separation of the most of
the suspended materials. From the liquid bottom a pumping station send the
settled material again to the dumping site. A second pumping station feeds the pretreatment unit. |
|
2) Pretreatment: pH correction and incondensable
elimination The settled waters are submitted to a double treatment for the
correction of its pH and the elimination of the incondensable. The pH
correction permit to block efficiently the dissolved ammonia. The
acidification process involves the developing of carbon dioxide that is
producing the formation of foam. The emissions into the atmosphere from the incondensable eliminatoion
process must be evaluated with a pilot plant, in order to caracterize the
kind of emission and the subsequen abatement plant. The following multi effects evaporation unit is designed to minimize
the energetic consumption of the second stage of the pretreatment. |
|
3) Multi effects vacuum evaporation The liquid that feeds the evaporation unit is taken from the second
stage of the pretreatment and is submitted to a vaccum distillation with
different vacuum degree in every single evaporation chamber. The process is
producing two different streams: v a distilled liquid
without any solids and with a low polluting charge, of about the 90% of the
treated quantity; v a turbid bottom
containing the most of the original pollutants, of about the 10% of the
treated quantity. |
|
4) Concentrated liquid feeding The concentrated bottom of the evaporator arrives to the starting
accumulation section and a pumping station feeds again this concentrated
liquid to the dumping site. |
|
5) Distilled product process stocking If further post treatments are needed, the distilled liquid is sent to
a series of process tanks. |
|
6) Osmotic membranes concentration The distilled liquid produced by the evaporators is treated on a
series of osmotic membrane filters to reduce further the residual ammonia
content. The osmosis permeate is collected in the accumulation tank and from
here sent to the pretreatment. The permeate can also be treated and purified with activated carbons and
is stored in a series of foreseen accumulation tanks. |
|
7) Treatment on activated carbon (compulsory in
presence of phenols) The distilled liquid from the evaporators, after the osmosis
treatment, is sent to a series of activated carbon vessels in order to reduce
further the dissolved organic substances content. The treated flow is after
sent to the final product stocking tank. The spent carbon is conferred to a Company with proper authorization
for its elimination and the carbon beds are, for consequence, to be changed
routinely. |
|
8) Stocking of the final treated liquid The distilled liquid, after the evaporation process and all treatments
is collected in a final storage tank. In consequence of its purity, this
final liquid can be classified as a liquid waste (to be conferred to a
Company with authorization for its destruction) or a normal discharge that
can be sent to the sewer system or to a surface water. |
The following Flow-sheet is reporting all the
processes employed to treat the percolate from a dumping site, for its
discharge in clear river waters, complying with the Law DL 152-2006 (ex DLgs
152-1999).
|
|
|
|
|
|
|
|
|
|
|
|