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Carbon Steel Slaughter Sewage Treatment Equipment 50T/D SQTZ-50
1, Design basis for slaughterhouse sewage treatment equipment
Management Measures for Environmental Protection of Construction
Projects (issued by the State Council Environmental Protection
Commission, National Planning Commission, and National Economic
Commission on March 26, 1986);
Regulations on Environmental Protection Management of Construction
Projects (passed at the 10th Executive Meeting of the State Council
on November 18, 1998);
The third level standard in GB13457-92 "Emission Standards for
Water Pollutants in the Meat Processing Industry"
Code for Design of Outdoor Drainage GB50014-2006;
The relevant data and materials provided by Party A.
2, Other specifications and standards for slaughterhouse sewage
treatment equipment:
Code for Design of Outdoor Drainage GB50014-2006;
Code for Structural Design of Water Supply and Drainage Engineering
(GBJ69-2002);
Code for Design of Industrial Corrosion Protection GBJ46-82;
Handbook of Industrial Pollutant Generation and Emission Factors;
Urban Regional Environmental Noise Standard GB3096-93;
Code for Design of Power Supply and Distribution Systems
(GB50217-94);
Code for Design of Building Water Supply and Drainage GB50015-2003;
Regulations on Selection of Automation Instruments (HG20507-92);
Code for Design of Low Voltage Electrical Installations
(GB50054-95);
Design Specification for Pump Stations GB/T50265-97.
3, Design principles for slaughterhouse sewage treatment equipment
Strictly implement national and local environmental, health, and
safety regulations, and after treatment, the main water quality
indicators meet relevant national standards;
Adhering to a scientific attitude in the design, the water
treatment process adopted should not only reflect advanced
technology, economic rationality, but also be mature, safe and
reliable, and have the characteristics of simple operation and
convenient operation and management;
The processing unit is relatively compact and occupies as little
land as possible, while ensuring stable operation and meeting the
standard of effluent quality, minimizing engineering and operating
costs as much as possible;
Adhere to the principle of combining sewage biochemical treatment
with ecological treatment in the design, and create a harmonious
ecological environment for sewage treatment.
4, Design and treatment scale of slaughterhouse sewage treatment
equipment
According to the provided information, the amount of slaughterhouse
wastewater is 200m ³/ d. Wastewater is mainly generated from
flushing water during pig slaughter, cleaning water for meat and
viscera after slaughter, and cleaning water for slaughtering
equipment and venues. Concentrated discharge of wastewater during
production.
5, Quality of inlet and outlet water from slaughterhouse sewage
treatment equipment
Based on the experience in slaughterhouse sewage treatment, the
quality of raw sewage before treatment in this project is shown in
the table below.
Unit:mg/L
Pollution factor quality | Design inlet water quality |
CODCr | ≤2000 |
BOD5 | ≤875 |
SS | ≤875 |
Animal and vegetable oils | ≤125 |
NH3-N | ≤100 |
pH | 6~9 |
Number of Escherichia coli | ≤ 20000 units |
Effluent quality requirements
The effluent quality indicators in this scheme design strictly
follow the third level standard in GB13457-92 "Water Pollutant
Discharge Standard for Meat Processing Industry".
Unit:mg/L
Pollution factor quality | Third level standard |
CODCr | ≤500 |
BOD5 | ≤300 |
SS | ≤400 |
NH3-N | - |
Animal and vegetable oils | ≤60 |
pH | 6.0~9.0 |
coliform group | - |
6, Analysis on the treatment process of slaughterhouse sewage
treatment equipment
Slaughtering wastewater contains pollutants such as animal blood,
oil, minced meat, food residue, pig hair, feces, and sediment. The
characteristics of wastewater can be summarized as follows: (1)
significant changes in water quality and quantity (the wastewater
from the factory is discharged in a centralized manner); (2) From
the quality of the original wastewater, it can be seen that the
wastewater has good biodegradability, with a B/C ratio of over 0.4,
making it suitable for biological treatment; (3) The suspended
solids content in wastewater is very high, with SS ≤ 1500mg/L. In
addition to inorganic impurity particles, there are also many
organic substances with poor fluidity such as lipids and proteins,
which account for about 40% -50% of CODCr. In this project, CODCr ≤
2000 mg/L, BOD5 ≤ 900mg/L, and animal and vegetable oil ≤ 125mg/L.
Based on the water quality, it can be seen that slaughterhouse
wastewater has good biodegradability, with turbid water quality,
easy to rot and odor, and forms scum, Pre treatment is necessary
before biological treatment.
The use of A/O biological treatment process has been the main
method used by domestic and foreign environmental protection
workers in recent years to solve wastewater denitrification. This
method has the following characteristics:
By utilizing the nitrifying bacteria and denitrification bacteria
cultivated in the system, the goal of removing carbon containing
organic matter and ammonia nitrogen in wastewater is achieved.
Compared with adding a denitrification tertiary treatment system
after ordinary activated sludge treatment, it has the advantages of
low infrastructure investment, low operating costs, low power
consumption, and less land occupation.
The A/O biological treatment system produces less excess sludge
than general biological treatment systems, and has good sludge
settling performance and is easy to dehydrate.
The A/O biological method has higher impact load resistance and
stable operation compared to general biological treatment systems.
The A/O biological treatment system converts NO2-N into N2, so
there is no accumulation of NO2-N generated during the
nitrification process. However, 1mg/NO2-N can cause a COD value of
1.14mg. Therefore, when only nitrifying, although the ammonia
nitrogen concentration may meet the standard, the COD concentration
often exceeds the standard seriously. Adopting an A/O biological
treatment system can not only solve organic pollution, but also
solve nitrogen and phosphorus pollution. In summary, through this
process flow, all indicators of the effluent can meet the third
level standard in the "Water Pollutant Discharge Standard for Meat
Processing Industry" GB13457-92.
7, Precautions for slaughterhouse sewage treatment equipment
(1) Animal hair, food residue, broken meat, bone residue, etc. are
prone to clogging the pump, which will affect the entire subsequent
process treatment. Therefore, mechanical grids are used in the plan
to remove the majority of suspended solids, impurities, etc.
(2) The organic matter content is high, and air flotation treatment
is used to remove most of the suspended solids and insoluble
organic matter, while reducing emulsified oil and improving the
impact of oil and fat in wastewater on subsequent fixed microbial
aeration biochemical unit treatment.
(3) Adopting a microbial aeration biochemical treatment system to
reduce pollutant concentration and increase nitrification stage to
improve wastewater treatment efficiency and ensure stable
operation.
(4) In order to further ensure that the water quality meets the
standards, this process adopts a combination of two physicochemical
and biochemical treatment processes to ensure that the effluent
meets the discharge standards.
8, Process flow design of slaughterhouse sewage treatment equipment
Process flow description:
Slaughtering wastewater is collected through a collection pipe
network and flows into a mechanical grid to remove large pieces of
meat, floating debris, and small suspended solids such as animal
hair. Then, it flows into an oil separation sedimentation tank to
separate and settle the oil, bone debris, sediment, and other
substances in the slaughtering wastewater. Then, it enters a pre
aeration tank for regulation. A microporous aeration device is
installed in the tank to regulate the water volume and homogenize
the water quality, The sewage is then lifted by the sewage pump and
enters the air flotation equipment. After the dosing reaction, the
sewage enters the mixing zone of the air flotation system and comes
into contact with the released dissolved water, causing the floc to
adhere to fine bubbles before entering the air flotation zone.
Under the action of air buoyancy, the floc floats towards the water
surface to form scum. The clean water in the lower layer flows to
the clean water tank through a water collector, and a part of it
flows back for dissolved air use. The remaining clean water flows
out through the overflow port. After the scum on the water surface
of the air flotation tank accumulates to a certain thickness, it is
scraped into the mud discharge area of the air flotation machine by
a foam scraper and then discharged into the sludge tank. The
dissolved air flotation machine mainly removes suspended organic
matter and oil substances. After treatment, it enters the
intermediate water tank to buffer the water volume and quality, and
then is lifted by the sewage pump to the hydrolysis acidification
tank. The hydrolysis acidification process is mainly used for
sewage treatment processes with high organic matter concentration
and high SS, and is a relatively important process. Hydrolysis
(acidification) treatment method is a method that falls between
aerobic and anaerobic treatment methods, and can be combined with
other processes to reduce treatment costs and improve treatment
efficiency. The hydrolysis acidification process controls anaerobic
treatment in the first and second stages of anaerobic treatment
with shorter reaction time based on the different growth rates of
methane producing bacteria and hydrolysis acid producing bacteria.
This involves the hydrolysis of insoluble organic matter into
soluble organic matter under the action of a large number of
hydrolysis bacteria and acidification bacteria, and the conversion
of difficult to biodegradable macromolecular substances into easily
biodegradable small molecule substances, thereby improving the
biodegradability of wastewater, Laying a solid foundation for
subsequent processing. After hydrolysis and acidification, the
sewage is pumped into an integrated sewage treatment equipment. The
microbial biochemical treatment unit inside the equipment removes
the remaining pollutants in the wastewater through biological
adsorption and degradation. The suspended solids and turbidity of
the effluent are close to zero, and the purified sewage is
disinfected and meets the standards before being discharged into
the municipal sewage pipeline network.