Title: Anaerobic Treatment
1Anaerobic Treatment
- PreetiBala Adatiya
- Lecturer
- School of Biotechnology
- DAVV
2Anaerobic Treatment
Anaerobik Aritma Biyoteknolojisi
The use of microbes in the absence of oxygen for
the stabilization of organic material by
conversion to methane, carbon dioxide, new
biomass and inorganic products.
Anaerobic treatment is most suitable for
wastewaters with COD concentrations in the high
strength range (gt2000 mg/l)
3Anaerobic Digestion Process
Anaerobik Aritma Biyoteknolojisi
4Anaerobic Digestion Process
- Three Mechanisms Occurring
- Hydrolysis Process conversion of insoluble high
molecular compounds (lignin, carbohydrates, fats)
to lower molecular compounds - Acidogenesis Process conversion of soluble
lower molecular components of fatty acids, amino
acids and sugars (monosaccharides) to lower
molecular intermediate products (volatile acids,
alcohol, ammonia, H2 and CO2) - Methanogenesis Process conversion of volatile
acids intermediate products to final product of
methane and CO2
Anaerobik Aritma Biyoteknolojisi
5ANAEROBIC SLUDGE DIGESTION
Anaerobik Aritma Biyoteknolojisi
- Anaerobic digestion is one of the oldest process
used for the stabilization of sludges. It
involves the decomposition of organic and
inorganic matter in the absence of molecular
oxygen.
6Process description
- In the anaerobic digestion process, the organic
material in mixture of primary settled and
biological sludges is converted biologically.
Under anaerobic conditions, to a variety of and
products including methane (CH4) and
carbondioxide. The process is carried out in an
airtight reactor. Sludge, introduced continuously
or intermittently, is retained in the reactor for
varying periods of time. The stabilized sludge,
withdrawn from the reactor, is reduced in organic
and pathogen content.
Anaerobik Aritma Biyoteknolojisi
7Anaerobik Aritma Biyoteknolojisi
- The two types of commanly used anaerobic
digesters are identified as - Standard-rate
- High-rate
8Standard-Rate Digester
- In the standard-rate digestion process the
contents of digesters are usually unheated and
unmixed. Detention times for the standard-rate
process vary from 30 to 60 days. - They are usually carried out as a single-stage
process. The functions of digestion, sludge
thickening, and supernatant formation are
carried out simultaneously. As a result of
digestion, the sludge stratifies by forming a
supernatant layer above the digesting sludge and
becomes more mineralized. As a result of the
stratification and the lack of mixing, not more
than 50 of the volume of a standard-rate
single-stage digester is used. Because of these
limitations, the standard-rate process is used to
small installations.
Anaerobik Aritma Biyoteknolojisi
9High-Rate Digester
- In the high-rate digestion process the contents
of digesters are heated and mixed completely. The
required detention time for high-rate digestion
is typically 15 days or less with the exception
of higher loading rates and improved mixing,
there are only a few difference between the
primary digester in a conventional two-stage
process and a single-stage high-rate digester.
Anaerobik Aritma Biyoteknolojisi
10- Two-stage digestion frequently, a high-rate
digester is coupled in series with a second
digestion tank. The first tank is used for
digestion and is heated and equipped wirh mixing
facilities. The primary function of the second
stage is to separate the digested solids from the
sopernatant, however additional digestion and gas
production may occur.
Anaerobik Aritma Biyoteknolojisi
11Process design
- An anaerobic digester is well mixed with no
liquid solids separation. Consequently, the
bioreactor can be treated as a continuous stirred
tank reactor (CSTR) in wich the HRT (hydraulic
retention time) and SRT (sludge retention time or
sludge age) are identical, the quantity of
methane gas can be calculate as below - VCH4 (L/day) 0,35 (L/gas)(EQS0-1,42Px)
Anaerobik Aritma Biyoteknolojisi
12AEROBIC SLUDGE DIGESTION
- Aerobic sludge digestion may be used to treat
only - waste activated sludge
- Mixtures of waste activated siudge and primary
siudge - Activated sludge treatment plant without primary
settling
Anaerobik Aritma Biyoteknolojisi
13Advantages
Anaerobik Aritma Biyoteknolojisi
- Volatile solids reduction is equal that obtained
anaerobically - Lower BOD concentrations in supernatant liquor
- Production of an odorless, humus-like,
biologically stable end - Operation is relativeluy easy
- Lower capital cost
14Disadvantages
Anaerobik Aritma Biyoteknolojisi
- A high power cost is associated with supplying
the required O2 - A digested sludge is produced with poor
mechanical dewatering characteristics - A useful by-product such as methane is not
recovered
15Process description
Aerobic digestion is similar to the
activated-sludge process. As the supply of
available substrate (food) is depleted, the
microorganisms begin to consume their own
protoplasm to obatin energy for cell maintenance
reactions when this occurs, the microorganisms
are ssaid to be in the endogenous phase.
Anaerobik Aritma Biyoteknolojisi
5CO2 NO3- 3H2O H
C5H7NO2 7O2
Cell tissue is oxidized aerobically to CO2 and
H2O and ammonia. The ammonia form this oxdation
is subsequently oxidized to nitrate.
16- An actuality, only about 75 to 80 percent of the
cell can be oxidized, the remaining 20 to 25
percent is composed of inert component. - A pH drop can occur when ammonia is oxidized to
nitarte if the alkalinity of the wastewater is
insufficient, chemical addition may be required. - Two variation of the process are commonly used
- conventional aerobic digestion (with air)
- high-purity oxygen aerobic digestion
- Aerobic digestion with air is the most commonly
used process.
Anaerobik Aritma Biyoteknolojisi
17Process design
- Factors taht must be considered in designing
aerobic digesters include - Solid reduction
- Hydraulic retention time
- Oxygen requirements
- Energy requirements for mixing
- environmental condition such as pH, temperature.
Anaerobik Aritma Biyoteknolojisi