Oxidization Tank
Waste water from the knit dyeing project destroy the quality of water body in which they are exposed affecting the marine life. It also has a harmful effect of sewerage handling system and agricultural land. The characteristics and effect of effluent are as follows
pH:
The waste water may be either acidic or alkaline.
If acidic
- It may cause corrosion of pipeline.
- Can cause destruction of aquatic life
If alkaline
- It may cause adverse effect on aquatic life
- Incrustation in sewers and damage corps by impairing their growth
DISSOLVE SOLIDS:
The dissolve solid may be either organic or inorganic. The can cause reduction in dissolve oxygen in waste water, disease and discomfort, scale in pipelines and other equipments, accelerate algal growth, increase hardness of water and enhance metal corrosion
SUSPENDED SOLIDS:
Suspended solids increase
- Turbidity
- Interferes light transmitting property of water
- Destroy photosynthesis and oxygen transmission process
Criteria | Average quality of textile effluent | Minimum std required to drain |
BOD | 300 mg/l | 20-40 mg/l |
COD | 1000 mg/l | 120-160 mg/l |
Suspended solid | 200 mg/l | 20-40 mg/l |
Settle able solid | 0-5 mg/l | No traces |
Ammonia | 20-30 mg/l | 4-8 mg/l |
Phosphorus | 3-5 mg/l | 3-5 mg/l |
Surfactant | 30-40 mg/l | 0.5-2 mg/l |
Chloride | 1000-1500 mg/l | 1000-1500 mg/l |
Sulphate | 1000-1500 mg/l | 1000-1500 mg/l |
Oil and fats | 30-40 mg/l | <5 mg/l |
Phenol | 3-5 mg/l | 0.05 mg/l |
color | colored | Not perceptible |
The Following standard is given by Bangladesh Department of Environment
Composite Textile Plant and large processing unit ( in which capital investment is more than thirty million taka)
Parameters | Standard and presence in a unit of mg/l |
pH | 6.5-9 |
Suspended Solid | 100 |
BOD5 20o C | 150 |
Oil and Grease | 10 |
Total dissolved solids | 2100 |
Wastewater flow | 100 |
Total Chromium as Cr | 2 |
Sulfide as S | 2 |
Phenolic Compounds as C6H5OH | 5 |
EFFLUENT TREATMENT AND DISPOSAL SYSTEM
In our country commercially Four-type process are available.
- Chemical process
- Biological process
- Chemical and biological combination process
- Chemical Biological and electro coagulation combined process
Typical operation involved in a ETP
CHEMICAL OXYGEN DEMAND-COD
This Means potential overall oxygen requirement of the waste water sample including oxidizable components not determined in the BOD analysis.
STEP | BLANK | SAMPLE |
1 | Take 20 ml DM Water in a conical flask | Take Sample in a conical flask as per dilution method |
2 | Add pinch of Mercury II Sulfate | Add pinch of Mercury II Sulfate
|
3 | Add 5 ml Silver Sulfate -Sulfuric acid solution | Add 5 ml Silver Sulfate -Sulfuric acid solution |
4 | Add 10 ml Potassium Dichromate solution | Add 10 ml Potassium Dichromate solution |
5 | Add 25 ml Silver Sulfate -Sulfuric acid solution | Add 25 ml Silver Sulfate -Sulfuric acid solution |
6 | Add glass beads | Add glass beads
|
7 | Reflux for 2 hours | Reflux for 2 hours
|
8 | cooling for 2 hours | cooling for 2 hours
|
9 | Add 80 ml Distilled water | Add 80 ml Distilled water
|
11 | Titrate with Ferrous Ammonium Sulfate
| Titrate with Ferrous Ammonium Sulfate |
12 |
TITRATION VALUE= A |
TITRATION VALUE= B
|
DILUTION METHOD
EFFLUENT | X-SAMPLE-ML | DISTILLED WATER-ML |
Collection Sump | 2 | 18 |
Clarifier Outlet | 5 | 15 |
UF permeate | 10 | 10 |
RO 1 feed | 10 | 10 |
RO 2 feed | 5 | 15 |
RO 3 feed | 5 | 15 |
RO reject | 2 | 18 |
Dye bath effluent | 1 | 19 |
NF permeate | 2 | 18 |
CHEMICAL OXYGEN DEMAND-COD
TITRATION
BURETT
0.1N ferrous ammonium sulfate
CONICAL FLASK
- X ml of sample
- 4-5 drops of Ferrion indicator
TITRATION
Sample Vs 0.1N ferrous ammonium sulfate
ENDPOINT
Bluish green to reddish brown
TITRATION | Titration of Blank | Titration of Sample |
Titration value | A | B |
CALCULATION OF COD -MG/LITRE
(A-B) X 0.1 X8 X1000
Xml OF SAMPLE
X -SAMPLE ML | CALCULATION – MG/LT |
1 | (A-B) X 800 |
2 | (A-B) X 400 |
5 | (A-B) X 160 |
10 | (A-B) X 80 |
15 | (A-B) X 53.33 |
BIOCHEMICAL OXYGEN DEMAND-BOD
Biochemical oxygen demand is the measure of the oxygen consuming capabilities of orange matter, water with high BOD indicates the presence of decomposing orange matter and subsequent high bacterial counts that degrade its quality and potential uses.
Solution A |
Blank |
Sample
|
Take 2 liter distilled water | Take 300ml A solution in BOD bottle without air make 2 sample | Take two sample without air, as per dilution method |
Aerate 1 hour | Check initial DO in one sample = B1 | Check initial DO in one sample= S1 |
Add 2ml ferric chloride | Another sample Keep in BOD incubator at 20’C For 5 days | Another sample Keep in BOD incubator at 20’C For 5 days |
Add 2ml magnesium sulfate | 20’C For 5 days
27’C For 3 days
| 20’C For 5 days
27’C For 3 days |
Add 2ml calcium chloride | After 5 or 3 days check DO | After 5 or 3 days check DO |
Add 2ml phosphate buffer |
DO of the blank is B2 |
DO of the blank is S2 |
Add 2ml seed solution
|
DILUTION METHOD AND ITS FACTOR
EFFLUENT |
SAMPLE-ML |
SOLUTION – A |
F |
P |
Raw effluent | 2 | 298 | 0.993 | 0.00667 |
Primary outlet | 5 | 295 | 0.983 | 0.01667 |
Secondary outlet | 10 | 290 | 0.967 | 0.03333 |
Ro 1 feed | 10 | 290 | 0.967 | 0.03333 |
Ro 2 feed | 5 | 295 | 0.983 | 0.01667 |
Ro 3 feed | 1 | 299 | 0.996 | 0.00333 |
TOTAL VOLUME = 300 ML |
BIOCHEMICAL OXYGEN DEMAND-BOD
CALCULATION
Blank solution do-sample do = (B1 – B2) – ((S1 – S2) F)
Dilution factor P
F- Fraction of sample to total volume = 300 – sample ml / 300
P- Fraction of sample to total volume = Sample ml /300
BOD SAMPLES TAKEN PROCEDURE
S.NO | BOD Range ( approx ) – mg/l | Volume of sample – ml
|
1 | 0-7 | 300 |
2 | 6-21 | 100 |
3 | 12-42 | 50 |
4 | 30-105 | 20 |
5 | 60-210 | 10 |
6 | 120-420 | 5 |
7 | 300-1050 | 2 |
8 | 600-2100 | 1 |
9 | 1200-4200 | 0.5 |
10 | 3000-10500 | 0.2 |
11 | 6000-21000 | 0.1 |
12 | 12000-42000 | 0.05 |
13 | 30000-105000 | 0.02 |
DISSOLVED OXYGEN-DO
STEP |
BOD BOTTLE |
1 | Take 300ml SAMPLE in BOD bottle without air
|
2 | Add 2ml manganous sulfate
|
3 | Add 2ml alkali iodide, sodium azide solution
|
4 | Immediately fix the stopper
|
5 | Keep 10 min for settling
|
6 | Add 2ml conc. Sulfuric acid
|
7 | Shake well
|
8 | Transfer 200ml in conical flask
|
9 | Titrate with 0.025 N sodium thio sulfate
|
BURETTE
0.025 N Sodium thio sulfate solution
CONICAL FLASK
- 200 sample
- 4-5 drops of starch indicator
TITRATION
Sample Vs 0.025 N Sodium thio sulfate solution
ENDPOINT Disappearance of dark blue
CALCULATION
TITRATE VALUE X 0.025 X8 X1000 -ppm
200 ml OF SAMPLE
TITRATE VALUE X 1 – ppm
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