EXAMPLE - LEATHER INDUSTRY: PELLNETA |
1.- INTRODUCTION AND BACKGROUND |
Environmental prevention and the minimisation of waste and emissions are based on the knowledge and understanding of the waste flows that are generated in the company's industrial processes and activities. The fact of having information on its waste flows and the cause of each one provides the enterprise with tools to carry out actions aimed at minimisation and cost saving Lack of knowledge is very often the main obstacle why enterprises fail to carry out actions in the area of pollution prevention. The purpose of this diagnosis is to establish potential opportunities for preventing pollution at source (reduction and recycling at source) and actions to be carried out that guide corporate policy in the direction of practices and technologies that make this viable. |
|||
2.- GENERAL DESCRIPTION OF THE COMPANY |
The product produced by PELLNETA is tanned and finished lambskin and goatskin. | ||
2.1.- Company details |
Company details | |
Company name |
PELLNETA
|
Appointee (legal representative) |
#
|
Fiscal identity number |
B-000000002
|
Main office address |
#
|
Telephone |
#
|
Fax |
#
|
e.mail |
#
|
Works address |
#
|
Municipality |
#
|
Post code |
#
|
Country |
#
|
Telephone | # |
Fax |
#
|
e.mail |
#
|
Data when carried out |
#
|
Year (data reference) |
#
|
Main activity |
Tanned
and finished lambskin and goatskin
|
Sector |
Leather
tanning
|
Classification of economic activity |
#
|
Turnover |
4.21
M€
|
Type of enterprise (small, medium, large) |
SME
|
Environmental policy of the company, programmes, resources allocated |
#
|
Contact persons |
#
|
2.2.- Human resources: structure and organisation. Conditions of work |
Human resources: structure and organisation | ||
Conditions of work | ||
Conditions of work | ||||||
Total workforce |
40
|
|||||
Distribution |
Office
|
Production
|
Maintenance
|
Warehouse
|
Others
|
|
#
|
#
|
#
|
#
|
#
|
||
Working hours |
Office
/ Administration
|
Plant
|
||||
#
|
From
6.00 to 22.00
|
|||||
Nº. working days / year |
227
|
|||||
Nº hours / year |
3,632
|
|||||
Seasonal variations - period of high activity |
#
|
|||||
Shifts and number of workers per shift |
During
period of high activity
|
Rest
of the year
|
||||
#
|
From
6.00 to 14.00From 8.00 to 12.00 and 14.00 to 20.00
|
|||||
Idle time in the company |
Holiday
periods
|
#
|
||||
Regular
stoppages
|
#
|
2.3.- Production (products) |
Information on the production process and raw materials was obtained from visits to the factory premises. | ||
2.4.- Raw and auxiliary materials |
The raw materials basically used by the PELLNETA company in the process of leather tanning are: lambskin, salts, acids and tanning substances. Aspects that may be relevant concerning alternatives have been identified for each of these as well as for the auxiliary materials. The main raw materials used appear in the following tables. |
||
RAW AND AUXILIARY MATERIALS | |||||||||||||||||||||
RAW AND AUXILIARY MATERIAL | Generic name |
SKIN
|
SALTS
|
ACIDS
|
TANNING
SUBS.
|
AUXILIARY
MATERIALS
|
|||||||||||||||
Unworked
raw lambskin
|
Wet-blue
lambskin/goatskin
|
Sodium
sulphide
|
Calcium
hydroxide
|
Codium
chloride
|
Sulphuric
acid
|
Formic
acid
|
Acetic
acid
|
Lactic
acid
|
Chromium
salts
|
Vegetable
tannins
|
Phenol-based
retanning agent
|
Phenol-based
retanning agent
|
Surfactants:
Humectants
|
Neutralising
salts: sodium bicarbonate, sodium formate, ammonium sulphate
|
Auxiliary:
Ammonia and different auxiliary materials
|
Fat-liquoring
materials: Grease, oils, fats (solid, paste, liquid)
|
Dyes
|
Finishing
products: Wax, casein, acrylic resins, nitrocellulosic lacquer, urethane,
solvents (ethyl alcohol, ethyl glycol)
|
Treatment
plant reagents: polyelectrolyte, coagulant, lime
|
||
Origin / Supplier |
Mediterranean
area
|
Spain
International |
Spain
|
Spain
|
Spain
|
NA *
|
|||||||||||||||
Annual quantity consumed |
240 000
hides/year
|
360 000
hides /year
|
4 800
kg/year
|
2 500
kg /year
|
-
|
12 100
kg/year
|
24 200
kg /year
|
#
|
#
|
#
|
#
|
#
|
|||||||||
Hazardous components for the environment |
#
|
#
|
Basic,
corrosive salts
|
Basic,
corrosive salts
|
Biological
treatment inhibitor
|
Very strong
acid
|
Organic
acid
|
Organic
acid
|
Organic
acid
|
Acid salts
with Chromium III
|
#
|
Acid and
toxic
|
Toxic
|
#
|
#
|
#
|
#
|
#
|
#
|
#
|
|
State of the product - Concentration - Texture |
50% salted
hides50% dry hides5-6 sq. feet/hide
|
Wet-blue5-6
sq. feet/hideor 4.5 sq. feet/hide
|
Solid
in flakes 60-62%
|
Solid
in powder form 90%
|
SolidFine
and coarse salt
|
Liquid
98%
|
Liquid
85%
|
Liquid
85%
|
LiquidCommercial
concentration
|
Solid33%
basicity
|
Solid
|
Liquid
|
Solid
|
#
|
#
|
#
|
#
|
#
|
#
|
#
|
|
Means of supply |
Wooden
pallets
|
Wooden
pallets
|
25 kg
plastic bags and 1 ton pallets
Packing: Retractable with plastic |
25 kg
paper bags and 1 ton palletsPacking: Retractable with plastic
|
25 kg
plastic bags
|
100 kg
plastic drums
|
One ton
plastic containers and 80 kg drums
|
Contenidors
plàstics de 80 kg o bidons metàl·lics 200-300 kg
|
80 kg
plastic drums
|
25kg paper
bags with plastic and on one ton wooden pallets.Packing: Retractable with
plastic
|
25 kg
paper bags and on one ton wooden palletsPacking: Retractable with plastic
|
One ton
containers
|
25 kg
paper bags and on one ton pallets
|
#
|
#
|
#
|
#
|
#
|
#
|
#
|
|
Means of storage |
Travelling
carriage
|
Travelling
carriage
|
Wooden
pallets
|
Wooden
pallets
|
Pallets
|
Manufacturing
section
|
Dyeing
Section
|
Dyeing
Section
|
Place
of use
|
Wooden
pallets in the chrome store
|
Wooden
pallets in the dyeing store
|
Dyeing
shed
|
Wooden
pallets in the dyeing shed
|
#
|
#
|
#
|
#
|
#
|
#
|
#
|
|
Means of transfer |
#
|
#
|
Manual
|
Manual
|
Manual
|
Manual
|
Manual
|
Manual
|
Manual
|
Manual
|
Manual
|
Manual
|
Manual
|
#
|
#
|
#
|
#
|
#
|
#
|
#
|
|
Process and/or areas where used |
All processes
|
All processes
|
Beam house
|
Beam house
|
Beam houseTanning
|
Beam house
|
Tanning
|
Dyeing
|
Tanning
|
Dyeing
|
Dyeing
|
Dyeing
|
Tanning
|
Tanning
Dyeing |
Tanning
Dyeing |
Tanning
Dyeing |
Dyeing
|
Finishing
|
Treatment
of effluents
|
||
Return of empty containers to the supplier |
#
|
#
|
NO
|
NO
|
NO
|
YES
|
YES
|
NO
|
NO
|
#
|
#
|
YES
|
YES
|
#
|
#
|
#
|
#
|
#
|
#
|
#
|
*NA: Data not available | ||
2.5.- Water consumption |
This company consumes a volume of 25,500 m³/year of water that comes from a municipal water supply company. 10% of these 25,500 m³ is used to produce steam in the production process, 89% is used directly in processes and 1% is for domestic and sanitary use. In this particular case, domestic and sanitary consumption has been taken to be 28.3 litres/person per day because only sanitary use is made of water; no other use is made under domestic and sanitary headings (showers, dish-washer, etc.). | ||
Water consumption |
Input | |||||||||
Municipal
Mains network
|
Surface
water catchment
|
Well
|
Tank
|
Internal
recycling
|
|||||
Consumption
|
%
|
Consumption
|
%
|
Consumption
|
%
|
Consumption
|
%
|
Consumption
|
%
|
25,500
m³/year
|
100
|
#
|
#
|
#
|
#
|
#
|
#
|
#
|
#
|
PRELIMINARY TREATMENT | |||||||||
# |
CONSUMPTION POINTS | |||||||||||
PRODUCTION
PROCESSES: Beam house, Tanning, Finishing
|
ENERGY
OR STEAM: Steam production
|
COOLING
WATER
|
INDUSTRIAL
CLEANING
|
EXCHANGE
REGENERATION
|
SANITARY
USE
|
||||||
Consumption
|
%
|
Consumption
|
%
|
Consumption
|
%
|
Consumption
|
%
|
Consumption
|
%
|
Consumption
|
%
|
22,695
m³/year
|
89
|
2,550
m³/year
|
10
|
#
|
#
|
#
|
#
|
#
|
#
|
225
m³/year
|
1
|
OUTPUT | ||
INCORPORATED
INTO PRODUCT
CLIENT |
PURIFICATION
TREATMENT
MUNICIPAL MAINS NETWORK |
AIR EMISSIONS
|
#
|
#
|
#
|
The cost of water | ||
This includes the direct cost of water (EUR 0.47/m³), the water rate (EUR 0.34/m³, according to the company's water use statement) and the cost of internal waste water treatment (EUR 0.72/m³), which in total is EUR 1.53/m³. | ||
The cost of water | |||
ITEM
|
BASE (m³/year)
|
€/m³
|
TOTAL €/m³
|
Water supply |
25,500
|
0.47*
|
11,985 €
|
Water rate
|
25,500
|
0.34**
|
8,670 €
|
TOTAL
|
25,500
|
0.81
|
20,655
|
*
Cost of the water supplied by the municipal water company. ** General charge established by the ACA + Specific charge established by resolution of the last water use statement presented. |
||
2.6.- Energy consumption |
This includes electrical energy consumption and other type of fuel and uses. The data for energy consumption by the PELLNETA company were not available. |
||
3.- DESCRIPTION OF THE INDUSTRIAL PREMISES |
The different sections in the company are as follows: - Loading and unloading depot o Beam house section - Dyeing section o Machining section - Suede section - Finishing section o Dispatch depot - Administration and offices - Laboratory |
||
4.- DESCRIPTION OF THE ACTIVITIES, MANUFACTURING PROCESSES |
AND/OR AREAS DIAGNOSED |
THE PELLNETA Company is a leather tanning company that specialises in the manufacture of hides for the manufacture of leather goods using lambskin and goatskin originating from Spain and abroad. There are four well-defined stages in the process of tanning hide. The first is receiving and preparing the hides, then tanning itself, then the dyeing of the hide in order to colour it and finally the finishing treatment. Each of these areas is subdivided into different individual operations, each with its own particular characteristics. |
||
4.1.- Production processes |
STORAGE OF UNWORKED HIDES | ||
Prior to the initial soaking operation, there is a series of basic steps that involve the job of storage or warehousing. | ||
Purchase of hides Transportation of the hides from the
place of origin to the factory Delivery and storage The hides are adequately preserved here
prior to beam house processing. From here, they can either be returned to the storage location or directly enter the beam house according to the demand for manufacturing. Beam house is the initial stage that hides are subjected to on arriving at a factory where the complete tanning process is undertaken, as is the case of this company. Each different step in the overall beam house stage is described below. |
||
BEAM HOUSE STAGE | ||
Beam house is the initial stage following the arrival of hides at a factory where the entire tanning process is undertaken, as is the case of this company. | ||
Soaking The objectives of this process are: - To moisten the hide and restore it to
a natural hydrated condition to prepare it for subsequent processes (dissolving
soluble proteins with water and neutral salts, albumins and globulins).
The change of soaking water is very important to eliminate salt in the fibres as water enters them as the salt dissolves. The equipment consists of three fixed brick-set
paddle vats that carry out one soaking operation per day, which enables
an average of 1050 hides a day to be treated. Water consumption is 10
m³ per operation. The purpose of the wool-removal operation is to loosen the roots of the wool so that it can be extracted mechanically without damaging the hide. The chemical attack that occurs is effective because the reducing agent loosens the roots of the wool. This chemical effect is usually combined with the physical effect of the machine that separates the wool and the hide; in the case of this company, however, the hides are painted and left. They are then put back onto the travelling carriage with a mild lime liquor. This operation is mechanical yet discontinuous and the machinery is very simple in that it merely consists of a belt which carries the hides and a sprinkler system from above from which sends out a spray of liquid sulphur and lime with a density of 15ºBe. All excess quantity falls on the tray where it drains into a tank and is recycled. The hides are placed with the flesh side facing upwards and the operation takes ten seconds. The line worker who is behind the machine folds the hides flesh to flesh and leaves them for 5-6 hours so that the reducing agent can take effect and attack the base of the hair follicles. The line worker then returns the hides to the paddle vat and as a result of the sulphur having attacked the base of the wool, it can be more easily removed in the following liming treatment. Sulphur paste is prepared in an appropriate
container for this purpose. Two people are necessary for the painting
operation, one to put the hides on the belt and the other to take them
off and fold them flesh to flesh. This involves immersing the hides in a bath of sodium sulphide for a specified period of time. The main objectives of liming are: - To loosen the fibrous structure of the
hide. 4 wooden drums with a 1:1 bath ratio (1
litre of water for each kilo of hide) are used for this. It is important for the hides not to be
scored or marked; for this reason great care is needed when adjusting
the machine. The equipment used for deliming is the
same as that for liming, i.e., 4 wooden drums with a 100% bath ratio.
Temperature conditions of 38-40ºC and a pH of 8.5 are essential in bating for maximum effectiveness of the pancreatic enzymes. Once the specified bating time is completed, the hides are checked and then put through a continuous cleaning process using cold water, the purpose being to cool the hides the hides and the bath and stop the enzymatic reaction. The cooling process is normally completed when the outflowing water temperature is similar to that of the inflowing water. Pickling The pickling process has various purposes. It is complementary to deliming in that it further reduces the alkalinity of the hides and brings them to the proper acid pH for tanning. |
||
- It also definitively inhibits the bating
effect due to the presence of salt and acid. |
||
The equipment used for pickling is a polyester tipper paddle vat where two operations are carried out per day and an average of 1,650 hides treated in each rinse. The bath ratio is 1 to 5, i.e. five quantities of water to one of hides. |
||
TANNING | ||
Once the hides have been picked, the tanning stage begins. This is divided into different separate operations: degreasing, tanning, roller pressing / classification, and chrome storage. | ||
Degreasing The purpose of degreasing is to eliminate the natural fat deposits in the hide, which facilitates regularity and thoroughness in the following process operations. The excessive presence of natural fat in the hide can lead to the following problems in the finished hide: |
||
- Dark stains |
||
For maximum efficiency, the degreasing process is carried out at between 30 to 35ºC temperature. An oxyethylenate nonylic-phenyl-based surfactant is used to emulsify the fat in the hide. Salt water at 7ºBe is used for the bath
to prevent swelling of the hides (following pickling). For this reason,
sodium chloride is added. The tanning process also gives the necessary feel and physical characteristics of leather and provides it with certain properties, such as homogeneity, feel, elasticity, grain, which are all achieved through one type of tanning or another and through the appropriate use of the different factors (temperature, pH, basicity, masking). When the hides have been degreased, cleaned and drained, the tanning bath is prepared. Given that the chrome salts are acid, salt water at a 7ºBe concentration is used for the bath. Formic acid is used to adjust the pH to 3.5 to improve penetration of the chrome salts, which are then added (in the form of chrome liquor). Sodium bicarbonate is used for basification to complete the fixing of the chrome salts. Once sufficient time has passed for the
hide to stabilise, check are made of the bath to verify correct exhaustion
and of the contraction temperature of the hide (over 100ºC). The hides
are finally rinsed so that they cool them and they are then loaded in
wagons. The hides are carefully covered with plastic sheeting to prevent them from drying out during storage. |
||
DYEING | ||
The third stage
in the factory's production process is the dyeing of the hides, which consists
of the following operations: skiving, neutralisation, retanning, fat-liquoring,
dyeing. A selection is made according to the clients' orders from the hides which are classified in chrome storage. |
||
Skiving / Neutralisation Once this mechanised operation is completed, the hide is then neutralised to correct the pH and prepare it for following operations. If a hide is not neutralised, the residual acidity of the hide, together with the presence of salts, specially sodium chloride, creates adverse conditions for the use of the leather and leads to the wear of seams and irritation when in contact with human skin. The products usually used for neutralisation are sodium bicarbonate, sodium formate and sodium carbonate. The use and proportions of these products varies according to the required article and the quality of hide. Following neutralisation, the hide is then
rinsed to eliminate any remains of neutral salts. The use of fats and oils on the hide maintains the fibres separate and lubricates them so that these slide smoothly against each other. Both synthetic and natural fats and oils
are used in an aqueous solution which is then pumped or applied manually
to the drum. Once the colouring has penetrated the hide, formic acid is added to pH 4 to fix and exhaust the bath dye stuff. The colour of the hide is then checked through comparison with the sample requested by the client and, if correct, it is washed in cold water to reduce the temperature of the bath and the hides. When the hides have cooled, they are loaded onto wagons and left for no longer than 24 hours. The equipment consists of 5 manually-loaded polyester and wood drums. |
FINISHING | ||
Finishing involves the final operations to the hides that give the end characteristics to the article. There are two subprocesses in the finishing stage: The first subprocess includes various different separate operations from when the dyed hides are unloaded to when they are pigmented. The second subprocess includes the operations following pigmentation through to dispatch. |
||
SUBPROCESS 1 | ||
The operations are as follows: rolling, checking, drying, conditioning, staking, toggling and trimming. | ||
Once the hide has been dyed and left to rest, it is put through a rolling process in a hydraulic machine. This operation mechanically reduces the moisture content of the hide and reduces the energy consumption involved with drying. When the hides have been roller pressed, a check is made so that the hides are stretched to the maximum before being dried. Drying reduces the moisture content of the hide and is carried out with a vacuum machine. The principle of vacuum drying consists of reducing the external pressure on the hide, which is enclosed in a hermetic container. A partial vacuum is created so that the water can evaporate faster and more easily at a temperature below 100ºC. Vacuum drying is applied so that hides do not sag. Once the hides are dried, they have to be conditioned prior to being staked. The fibres in the hide join together during the drying process, which produces a hard, compact hide. The dried hide cannot be directly staked because this would cause the fibres to break and produce a spongy hide. In order to avoid this, the hide is conditioned until there is a homogenous humidity content of 20-22% throughout the entire thickness of the hide. The system used for conditioning the hides is very simple in that they are placed on a conveyor belt that passes beneath a series of sprinklers whereby they get covered by the spray of water. The moistened hide is put on the travelling carriage and left for some time under plastic sheeting in order for the moisture to spread in a uniform way. Staking is a mechanical operation that makes the hide flexible. The type of staking is done with a pivot machine. This machine transports the hide on two rubber belts that pass through parts with vibrating pivots. The level of percussion can be regulated independently for each hide, which enables the intensity of staking to be achieved for each area of the hide. Toggling is done after the mechanical process of staking because the hides need to be dried while they are kept flat until the final moisture content is reduced to approximately 10-12%. Unusable parts for manufacture are then trimmed using scissors, including marks from drying pegs, areas with defects or cuts, etc., the purpose being to improve the class of the hide and to improve its machineability. The following operations are also carried out on certain types of hide: Buffing is used to produce suede
articles, to clean the edges of the leather on articles, to manufacture
nubuck, etc. A large amount of dust is produced during the buffing operation, part of which adheres to the hide due to electrostatic load. Given that the dust has to be totally eliminated in order to finish the hides (irregularities would develop in the finish if not), the dust is removed (dusting). The company has a brush-type dusting machine, the workings of which are very simple. It consists of two cylinders with brushes that rotate in opposite directions and the hide is placed between the two. |
SUBPROCESS 2 | ||
The second finishing subprocess includes all of the operations between pigmentation and dispatch, both of these included. The separate operations in this second process are: product application, drying, polishing and glazing, ironing, measurement and classification. | ||
The purpose of product application is to give the surface of the hide the appropriate colour and glossy finish. The products are applied in this company using rotary air-brushes. Products used for finishing include pigments, dye and colouring matter, resins, wax, lacquer and casein. Spray-applied pigments are used to obtain very light, uniform coatings that do not overload the grain while highlighting the quality of the hide. The main purpose of drying is to evaporate the water, solvents and diluents used to prepare and apply the finishing. The drier consists of different independent elements assembled consecutively along the conveyor, with a total drying capacity in line with the application system. The hides are stacked when they come from the pigment coating machines and drying line prior to polishing and glazing. Polishing and glazing are applied according to the type of hide and the article required. Glazing is exclusively for finishes
with proteinic bonds and gives a very characteristic aspect that even
today is irreplaceable. The glazing operation is done using a machine
with an arm that has a glass cylinder on the carriage that quickly slides
under pressure to produce a shine and feel that is totally different from
that achieved with other machines. Ironing is to ensure the correct fixing of the different products that have been applied. The hide is placed in an ironing machine which has two cylinders that compress the hide as they turn in the same direction. One of the cylinders is metallic and incorporates a heating system whereby the hide is pressurised and heated along the line of contact with the cylinder as the machine turns. The finished hides are merchandised according
to surface area and therefore need to be measured. This process
is carried out with an electronic machine consisting of: The hide is placed as flat as possible on a frame-type conveyor belt that passes beneath the measurement header in the middle. A system of photoelectric cells reads the surface of the hide, which is then automatically marked on the back-side of the hide. Once the hides have been measured, they are classified according to the characteristics requested by clients and the different classes of hide are then stored in the dispatch storage location. When an order comes in, the hides are packed in different sized cardboard boxes. These boxes are folded and printed on arrival and the only operation required is manually opening them out, packing the hides and sealing the boxes. |
4.2.- Effluent treatment process |
The PELLNETA company uses a physiochemical treatment process to purify its waste water. | ||
This physiochemical treatment consists
of the following stages: The characteristics of the tank are as follows: |
CHARACTERISTICS | |||||||
Material
|
Reinforced
concrete.
|
||||||
External
diameter
|
15 m
|
||||||
Internal
diameter
|
6 m
|
||||||
Depth
|
5 m
|
||||||
Capacity#
|
750
m³ (approx.)#
|
Coagulation-flocculation chamber: The systems used to prepare both the coagulant and the flocculent are described below. |
Preparation and dosage of coagulant: | Preparation and dosage of flocculating agent: | ||
Tank made
of
|
Polyethylene
|
Tank made
of
|
Polyester
reinforced with fibre glass
|
Capacity |
500
litres
|
Capacity |
1,000
litres
|
Units
|
1
|
Units
|
2
|
System agitation |
Mechanical
|
System agitation |
Mechanical
|
Concentration coagulant |
20%
volume
|
Flocculent concentration |
0.1%
|
Coagulant |
Chargepac
300
|
Flocculent |
Anionic
polyelectrolyte
|
Pump type |
Membrane
|
Pump type |
Membrane
|
Model |
RB 25
A 95 DV
|
Model |
RB 43
A 70 DV
|
Volume |
32 l/h
a 10 mca
|
Volume |
75 l/h
a 10 mca
|
Current
setting
|
24%
|
Current
setting
|
30%
|
Separation: The flushed water goes to the sewer system
which leads to the municipal treatment plant while the sludge is pumped
to the sludge thickener. The ferric chloride is pumped by a 0'5" pneumatic pump and is taken from the tanks. Liming is prepared as follows: |
Sludge preparation | |
Tank material
|
Polyester
reinforced with fibre glass
|
Capacity |
1,000
litres
|
Units
|
2 (one
is not used)
|
System of agitation |
Mechanical
|
Lime concentration |
10%
|
Pump type |
Pneumatic
|
Model |
1"
|
Volume |
Variable
according to pressure
|
Sludge dehydration: The dehydration system is described below: |
Dehydration system | |
Dehydration
system
|
Filter
press
|
Type |
Automatic
|
Plate
size
|
630
x 630
|
No. plates |
60
|
Filtering capacity |
475
kg/filter
|
Pump drive |
Pneumatica
|
Size and type |
2" iron
foundry
|
5.- WASTE FLOWS: NUMBER AND DESCRIPTION OF WASTE |
FLOWS GENERATED - THE CAUSES OF WASTE FLOW GENERATION |
- CURRENT MANAGEMENT PRACTICE |
5.1.- Input of waste flow / environmental vector |
# | # |
Emissions
|
Waste
water
|
Waste
|
Storage
of raw, unworked hides
|
Removal
of unusable parts
|
Steam boilers Pigment coating machines and pigmentation driers
|
Waste water
-
4 baths x 10m³/rinse ** Waste water - 1 m³ day** Waste water - 30m³ day** Waste water - 1m³ day** Waste water - 10m³/process** Waste water - 15m³/process** Waste water - 5m³/process** Waste water - 15m³/rinse** Waste water - 7m³/rinse** Waste water - 40m³/process** Waste water - insignificant |
Unusable
wooden pallets Raw hide offcuts 24.74 tons/year Preervation salts for hides
Plastic wrapping for pallets Empty plastic bags (sodium salts) Damaged wooden pallets Plastic wrapping for pallets Empty plastic bags (sodium salts) Damaged wooden pallets Fleshings Empty plastic bags Damaged wooden pallets Empty plastic bags Damaged wooden pallets Empty enzyme containers Empty containers Empty containers Empty plastic bags Damaged wooden pallets Plastic containers Plastic bags Damaged wooden pallets Containers for colouring matter, retanning agents and fat-liquors Damaged wooden pallets Finishing products containers Sludge: 44.5 tons/year |
Beam house
|
Soaking
|
|||
Painting
|
||||
Dehairing
/ Liming
|
||||
Deliming
|
||||
Fleshing
|
||||
Bating
|
||||
Pickling
|
||||
Tanning
|
Degreasing
|
|||
Tanning
|
||||
Dyeing
|
Neutralisation -
Retanning-Dyeing- Fat-liquoring - |
|||
Finishing
|
1st subprocess
|
|||
2nd subprocess | ||||
Effluent
treatment
|
* Not assessed individually |
Definition of the most important waste flows will depend on the cost of their management and improvements of any type often have a direct effect on this. Waste that is recovered (either internally or externally) is not a cost for the company and in certain cases can even lead to income if the waste is sold to another company. In this particular case, the only cost is that of non-selectively collected waste and the effluent treatment sludge. Costs are accounted for by the transportation and disposal on the corresponding controlled landfill site. |
Emissions into the air | ||
In this case, there are two types of source: Pigment coating machines and pigment dryers used in processing. |
Emissions into the air | |||||
Point source | Pigment coating machines 1.2 | Steam boiler 1 | Steam boiler 2 | #Pigment dryers 1.2 | |
Origin | Production process | Energy generators | Energy generators | Others | |
Emission | Hours/day | 14 | 14 | 14 | 14 |
Days/year | 227 | 227 | 227 | 227 | |
Frequency | Discontinuous | Continuous | Continuous | Discontinuous | |
Output temp. ° C | - | 186º C | 290º C | 80º C | |
Pollutants | Hydrocarbons | SO², CO | SO², CO | Hydrocarbons | |
Fuel | - | Gas-oil | Natural gas | - |
Waste water | ||
Waste water is often one of the most important waste flows. This company channels all waste water from the different separate processes (beam house, tanning, dyeing, finishing and domestic and sanitary use) into a physiochemical purification system located next to the factory, within the grounds of the company. The water ends up in the municipal sewerage system whereby the water enters the municipal treatment plant. |
Waste water | |||||||||||||
Outlet point |
1
|
||||||||||||
Origin |
B E A
M H O U S E
|
TA N N
I N G
|
DYEING
|
FINISHING
|
SANITARY
|
||||||||
Soaking
|
Wool removal
|
Liming
|
Fleshing
|
Deliming
|
Bating
|
Pickling
|
Degreasing
|
Tanning
|
|||||
Volume or Quantity(1) |
4 x 10
m³/day x 3 paddle vats
|
1m³/day
|
30
m³/day
|
1m³
/day
|
10
m³/process
|
15
m³/process
|
5m³/process
|
15
m³/rinse
|
7m³/rinse
|
40
m³/process
|
Insignificant
|
255
m³/year
|
|
Treatment |
Physiochemical
|
||||||||||||
Type |
High salt
concentration Impurities: blood, excreta, fur, organic elements and preservatives
|
High
sulphur content
|
High
alkalinity, proteins, fats
|
Remains
of glandular tissue, proteins and fatty matter
|
High
soluble calcium salt content
|
Pigmenting
substances, soluble proteins, high nitrogen content
|
High
concentration of sodium chloride and acids
|
High
concentration of salts, high acidity, high solvent content, emulsified
substances and fat
|
High
concentrations of chemical products, chrome salt, leather fibres, emulsified
fat
|
Surfactants,
emulsified fat-liquors, colouring matter, neutral salts and retanning
agents
|
#
|
#
|
|
Destination |
Municipal
sewerage system (treatment plant)
|
||||||||||||
Cost |
0.72 €/m³
Total 25,755 m³/year 18,544 €/year |
(1) The annual quantity of waste water is 25,500 m³ from production processes and 255 m³ from domestic and sanitary activities. | ||
Waste | ||
The main forms of solid waste generated by this company are plastic containers, hide offcuts and shavings, fleshings, non-selective collection waste, effluent treatment sludge, which are sent to landfill on a controlled site. |
Waste | ||||||
Description |
Origin
|
Classification
|
Quantity
|
Management
actual
|
Cost
|
|
Non-returnable plastic containers |
Chemical
products
|
Hazardous
|
547 u/year
|
Recovery
|
No cost
|
|
Returnable plastic containers |
Chemical
products
|
Hazardous
|
840 u/year
|
Returned
to suppliers
|
No cost
|
|
Hide offcuts and shavings |
Hide offcuts
Hide skiving |
Non-hazardous
|
24.74
tons/year
|
Recovery
|
No cost
|
|
Glandular material |
Fleshing
of hides
|
Non-hazardous
|
ND* tons/year
|
Recovery
|
#
|
|
Non-selective collection waste (1) |
Waste
generated in the factory
|
Non-hazardous
|
195.26
tons/year
|
Controlled
landfill
|
Transport
12.92 €/ton
Management 27.11 €/ton TOTAL 7,815.75 €/year |
|
Effluent treatment sludge |
Physiochemical
treatment
|
Non-hazardous
|
44.5 tons/year
|
Controlled
landfill
|
Transport
12.02 €/ton
Management 38.16 €/ton TOTAL 2,233.21 €/year |
* Data not available (1) Raw hide offcuts, unusable wooden pallets, conservation salts, retractable plastic pallet wrapping, empty plastic bags, damaged wooden pallets, etc. |
||
5.2.- Input per process |
In order to clearly and precisely number and describe the different waste flows generated in the factory, the following different processes and sections are considered below: beam house, tanning, dyeing, and finishing. | ||
RAW, UNWORKED HIDE STORAGE LOCATION | ||
The only waste flows generated in the raw, unworked hide storage location is the offcuts of unusable parts of the hide (heads, rough wool), conservation salt that falls from the hides when being trimmed, and the wooden pallets, which are impregnated with the smell of hide and cannot be used for finishing processes. Neither can they be recovered. | ||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity
|
Management
|
Cost
|
|
1 | Offcuts of the unusable parts of the hide |
Solid
waste
|
Not assessed
individually
|
Landfill
|
40.03
€/ton
|
|
2 | Unusable wooden pallets |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
3 | Conservation salts |
Solid
waste
|
Not assessed
individually
|
Landfill
|
BEAM HOUSE | ||
As is described
above under the production process, beam house consists of different separate
activities, each of which generates a different waste flow. These are all
explained below. Sub Process - Soaking Only waste water is generated in this operation from the soaking of the hides. However, the rinses generate large quantities of waste water (10m³/rinse) which have a neutral pH or are slightly acid or alkaline, depending on the auxiliary materials used, and a high concentration of salt and the remains of impurities such as blood, excreta, fur and other organic elements and preservatives. All of the water is subjected to a physiochemical treatment in the company's own purification plant. |
||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity (1)
|
Management
|
Cost
|
|
1 | 1st rinse |
Waste
water
|
10 m³/rinse
|
Physiochemical
treatment
|
40 m³/paddle
vat
3 paddle vats EUR 0.72 /m³ 100 rinses/year ->EUR 8,640 /year |
|
2 | 2nd rinse |
Waste
water
|
10 m³/rinse
|
Physiochemical
treatment
|
||
3 | Soaking bath |
Waste
water
|
10 m³/rinse
|
Physiochemical
treatment
|
||
4 | Final rinse |
Waste
water
|
10 m³/rinse
|
Physiochemical
treatment
|
(1) Data for one paddle vat | ||
Sub Processes
- Removal of the wool Waste flows in the wool-removal process include the plastic wrapping of the pallets containing the bags of sodium sulphide, the remains of plastic bags for sodium sulphide, damaged wooden pallets and waste water from the cleaning of the painting machine. These rinses generate very little volume of water (approximately 1m³/day) but the effluents are highly alkaline due to the sodium sulphide and the calcium hydroxide that make up the paint paste for removing the wool. This water also logically contains a high sulphur content. This waste water is redirected to the company's physiochemical purification plant where the appropriate treatment is applied. |
||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity
|
Management
|
Cost
|
|
1 | Plastic retractable wrapping from the sulphur pallets |
Solid
waste
|
Not assessed
individually
|
Landfill
|
40.03
€/ton
|
|
2 | Empty plastic bags (sodium sulphide) |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
3 | Damaged wooden pallets |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
4 | Cleaning water from the paint machine |
Waste
water
|
1 m³/day*
|
Physiochemical
treatment
|
0.72 €/m³ |
* Estimated data | ||
Sub Process Dehairing
/ Liming The main form of waste generated by this process are the remains of plastic bags that have contained sodium sulphide, unusable wooden pallets and the water from the rinses. |
||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity
|
Management
|
Cost
|
|
1 | Plastic bags |
Solid
waste
|
Not assessed
individually
|
Landfill
|
40.03
€/ton
|
|
2 | Plastic bags Unusable wooden pallets |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
3 | Water from the rinsing |
Waste
water(1)
|
30 m³/daya*
|
Physiochemical
treatment
|
0.72 €/m³
|
(1) Although the volume of water generated
in this operation is not so high as in beam house processes (approximately
30m³/day), its pollution load is very important. The water is highly alkaline,
there are remains of proteins and small quantities of fatty material that
are sent to the company's own treatment plant. |
||
Sub Processes
- Fleshing The main waste produced is the fleshings extracted from the hide which are recovered externally. |
||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity
|
Management
|
Cost
|
|
1 | Fleshings |
Solid
waste
|
NA*
|
Recovery
|
-
|
|
2 | Water originating from fleshing |
Waste
water (1)
|
1m³/day**
|
Physiochemical
treatment
|
0.72
€/m³
|
* Data not available
** Estimated data (1) Waste water from this process basically contains remains of fleshings, together with proteins and fat. The volume generated is not important (1m³/day) which is also sent to the company's own physiochemical treatment plant. |
||
Sub Processes:
Deliming The main waste flows generated in this process are the remains of the plastic bags containing sodium sulphide, damaged wooden pallets and waste water from the rinses. |
||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity
|
Management
|
Cost
|
|
1 | Plastic bags |
Solid
waste
|
NNot assessed
individually
|
Landfill
|
40.03
€/ton
|
|
2 | Damaged wooden pallets |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
3 | Water from rinsing |
Waste
water (1)
|
10m³/process
*
|
Physiochemical
treatment
|
0.72 €/m³
|
* Estimated data ( 1) The volume of waste water generated in this process comes from rinsing and has a high soluble calcium salt content. The volume generated is 10 m³/process which is treated in the company's own physiochemical treatment plant. |
||
Sub Processes
- Bating The main waste flows generated in this process are the empty containers of the pancreatic enzymes, the empty sacks of ammonium sulphate, damaged wooden pallets and the plastic retractable wrapping for the pallets as solid waste, which are sent to landfill on a controlled site, and the waste water generated in the rinses. |
||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity
|
Management
|
Cost de gestió
|
|
1 | Empty enzyme containers |
Solid
waste
|
Not assessed
individually
|
Landfill
|
40.03
€/ton
|
|
2 | Empty plastic bags (ammonium sulphate) |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
3 | Damaged wooden pallets |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
4 | Plastic retractable wrapping for the pallets |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
5 | Cleaning water |
Waste
water(1)
|
15 m³/process*
|
Physiochemical
treatment
|
0.72 €/m³
|
* Estimated data
(1) This water (15m³/process) contain pigments, soluble proteins and a high nitrogen content from the ammonia salts. The water is very slightly alkaline. |
||
Sub Processes
- Pickling Two types of waste flow are generated in this process, a solid waste flow consisting of empty sulphuric acid containers, which are recovered externally, and a liquid waste flow comprised of waste water from the emptying of the pickling solution (5m³/process), which is sent to the company's treatment plant. |
||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity
|
Management
|
Cost
|
|
1 | Empty H2SO4 containers |
Solid
waste
|
Solid
waste Included under plastic containers
|
External
recovery
|
None
|
|
2 | Pickling solution |
Waste
water (1)
|
5 m³/procés
*
|
Physiochemical
treatment
|
0.72
€/m³
|
* Estimated data |
||
TANNING | ||
The tanning stage
consists of different separate operations that are clearly shown in the
diagram on the following page. The waste flows that are generated are also
described below. Sub Processes - Degreasing The waste flows here are, on the one hand, empty containers for degreasing products and the remains of plastic bags containing sodium chloride and, on the other, waste water from the emptying and rinsing of the degreasing bath, which are calculated as 15m³/rinse. |
||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity
|
Management
|
Cost
|
|
1 | Empty containers - degreasing products |
Solid
waste
|
Not assessed
individually
|
External
recovery
|
No cost
|
|
2 | Vacuuming and degrease rinsing water |
Waste
water (1)
|
15 m³/rinse*
|
Physiochemical
treatment
|
0.72 €/m³
|
* Estimated data (1) This water has a high saline concentration, it is highly acidic (pH 3-4), and it has a high content of solvents, emulsifying agents and fat. As with the other waste water flows, it is sent for physiochemical treatment in the company's own plant. |
||
Sub Processes
- Tanning As in the other processes, the solid waste is made up of plastic bags that contained chrome salts, damaged wooden pallets and the packaging of acids, which are all sent to landfill on a controlled site. Waste water is generated from the rinsing in the final stage of this process. |
||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity
|
Management
|
Cost
|
|
1 | Plastic bags (chrome salts) |
Solid
waste
|
Not assessed
individually
|
Landfill
|
40.03
€/ton
|
|
2 | Damaged wooden pallets |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
3 | Containers |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
4 | Rinsing water from chrome tanning |
Waste
water (1)
|
7 m³/rinse*
|
Physiochemical
treatment
|
0.72 €/m³
|
* Estimated data |
||
DYEING SUB PROCESS NEUTRALISATION -RETANNING - DYEING - FAT LIQUORING | ||
The dyeing stage consists of the following operations: neutralisation; retanning; dyeing; and fat-liquoring. Solid waste that is generated consists of plastic bags that contain the neutralisation salts, damaged wooden pallets and the plastic containers for the dyes/colouring matter, retanning agents and fat-liquors. There is also an aqueous waste flow from rinsing following neutralisation, fat-liquoring and dyeing. |
||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity
|
Management
|
Cost de gestió
|
|
1 | Plastic bags (neutralisation salts) |
Solid
waste
|
Not assessed
individually
|
Landfill
|
40.03
€/ton
|
|
2 | Damaged wooden pallets |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
3 | Containers of dyes, retanning agents and fat liquors |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
4 | Rinsing water from neutralisation, fat-liquoring and dyeing |
Waste
water (1)
|
40 m³/process*
|
Physiochemical
treatment
|
0.72 €/m³
|
* Estimated data |
||
FIRST FINISH ACCORDING TO EACH SUBPROCESS | ||
Bearing in mind that there are two finishing processes, the waste flows that are generated consist of damaged wooden pallets, plastic packaging from the different products used and waste water in both conditioning in the first subprocess and the application of products in the second subprocess. The volume of waste water in the finishing process is insignificant. As the products are applied using rotary air-brushes, a very light quantity waste is produced by coatings that do not directly come in contact with the hide. These coatings are collected by paper at the bottom of the pigment coating machine and basically contain pigments, colouring matter, resins, wax, lacquer, casein, solvent and fixative. | ||
ÉS | ||||||
Nº | Waste flows |
Type
|
Quantity
|
Management
|
Cost
|
|
1 | Damaged wooden pallets |
Solid
waste
|
Not assessed
individually
|
Landfill
|
40.03
€/ton
|
|
2 | Finishing product containers |
Solid
waste
|
Not assessed
individually
|
Landfill
|
||
3 | Water from conditioning |
Waste
water
|
Insignificant
|
Physiochemical
treatment
|
0.72 €/m³
|
6.- MINIMISATION OPPORTUNITIES AND PROPOSALS. DESCRIPTION OF THE |
RECOMMENDED ALTERNATIVES AND THEIR TECHNICAL FEASIBILITY |
AND ECONOMIC VIABILITY |
Finally, mention is made of the recommended minimisation opportunities obtained as a result of this study. | ||
RECYCLING THE LAST RINSE OF THE
SOAKING OPERATIONS |
6.1.- Recycling and recovery: recycling the last rinse |
of the soaking operations |
In the soaking operation, a large volume of water is generated which has a neutral pH and contains soluble proteins, remains of blood, excreta, sodium chloride, naphthalene and other preservatives, according to the type of hide being worked. Prior to soaking as such, the hide is rinsed
twice and then soaked in a final rinse. These rinses consist of filling
the paddle vat, mechanically stirring the hides and then emptying the
vat. The water from the last rinse in the soaking operation has a low salinity (0.3ºBe), which means that it can be reused. |
RECYCLING THE LAST RINSE OF THE SOAKING OPERATIONS | ||||||
Proposal description | Objective: | Recycling the water from the last rinse in the soaking operation has a low salinity, neutral pH and the presence of soluble protein, which enable it to be reused. | ||||
Description | # | |||||
Technical feasibility | Technique | 100%
recycling of the volume of water is envisaged. These data were obtained
from tests carried out on site to check that recycling of all of the water
does not negatively affect the quality of the end product, which were backed
up analytical assays. In order to be able to use this water, the facilities need to be adapted so that the water is sent from the last rinse to a polyester tank, which can be set next to the paddle vats, and then via a pumping system into the paddle vat to start the following process. |
||||
Equipment: | 20m³
polyester tank Mechanical agitator Centrifugal impulsion pump Milling Valves and piping |
|||||
Raw materials and/or processes affected | Processes affected: soaking operations | |||||
% reduction in the waste flow | A saving of water equal to the volume of water used in the final rinse (10 m³/paddle vat) is anticipated. | |||||
Other waste flows affected | # | |||||
Variation in production capacity | # | |||||
Others | # | |||||
Balance | Economic Viability | # | Material | Quantity | Unit cost | Total cost |
Saving | Water | 10
m³/rinse 3 paddle vats 227 days/year 40% raw hides -> 10 X 3X 227x 40% = 2,724 m³/year |
0.81 €/m³ | 2,206.44 €/year | ||
Waste water | Water saved : 2,724 m³ | 0.72 €/m³ | 1,961.28 €/any | |||
New costs | # | |||||
Total saving |
4,167.72
€/year
|
|||||
Investment | EQUIPMENT PURCHASE | 20m³
polyester tank + mechanical agitator + centrifugal impulsion pump + milling Valves and piping = EUR 6,611.13 |
||||
Service connection | # | |||||
Engineering | # | |||||
Others | # | |||||
Investment payback period | 6,611.13 / 4,167.72 = 1.6 years | |||||
Observations/other issues to be considered | # |
6.2.- Process modification - change of technique : hot chrome tanning |
Chrome tanning is usually one of the most inefficient operations and, depending on the method, the theoretical use of the chrome used is from 15% to 70%. A large amount of the chrome salts added to the bath are therefore lost, which represents an unnecessary cost, as well as large quantities of chrome salts being transferred to the waste water (3,085 kg of commercial chrome salt per ton of pelt). As well as the cost of these kilos of unused chrome salts, there is also the cost of recovery, if this is done in the facilities, or purification treatment of the sludge that is produced. The parameters that condition the efficiency of tanning by modifying the capacity and/or rate of reaction between the hide and the chrome salt have been known for a long time. Some are due to the hide itself and the pretreatment processes such as compactness, thickness, intensity and duration of the liming process, bating and pickling, as well as the types of acid used. Others factors play a role during the tanning process: pH and acidity, quantity and type of neutral salt, quantity and basicity of chrome salt, the degree of masking and fat-liquoring, the bath volume and chrome concentration, the mechanical effect, temperature, the length of time, etc.. Of all of the factors mentioned above, the influence of temperature is one of the most important. For example, for a set period of time, chrome fixation in the hide will vary according to the temperature. Furthermore, the fixed chrome is more stable, resulting in a reduced need for rinsing in subsequent operations. The temperature also considerably increases
the speed of the tanning process, in that: |
||
At 20ºC, 48 hours are necessary
for a cT of 100ºC. At 40ºC, 8 hours are necessary for a cT of 100ºC. At 50ºC, 4 hours are necessary for a cT of 100ºC. |
||
cT represents the contraction temperature. It is a measurement of the state of tanning and the hide's resistance. As the temperature of the bath increases, less time is needed to achieve the same tanning quality. |
HOT CHROME TANNING | ||||||
Proposal description | Objective: | Increase tanning efficiency by increasing the temperature. Reduce chrome consumption | ||||
Description | It is difficult with both small and especially large hides to go from end temperatures higher than 37ºC by the simple transformation of mechanical friction with heat, even after a long period of time (16-18 hours). A external heat source programmed according to the increase in the contraction temperature of the hide, or in other words the degree of tanning, could shorten the process, at the same time that automation would increase the uniformity between different batches.(1) | |||||
Technical feasibility | Technique | Treatment
is by way of a heat exchanger installed in the recycling system to provide
the necessary 50-60 Kcal for taking 1 kg of pelt from the initial 25ºC to
an end temperature of 42-44ºC. Thermal applications are made after the heat
exchanger has been on for an hour, by which time the total cross-over will
have been achieved, and are divided over the following 4-6 hours according
to temperatures preset in a small programmer, and measured so that the thermal
salt does not exceed 5ºC (difference of temperature between when the bath
enters the heat exchanger and when it comes out hot). The mechanism is relatively
simple and easy to install in drums or a mixer with recycling. The drums used for chrome tanning by the company at the present time do not incorporate recycling. A recycling system with a heat exchanger would therefore need to be installed to be able to gradually heat the bath. In this particular case, adaptation of the tanning drums is proposed. The capacity of each is 4,000 litres. |
||||
Equipment: | Heat
exchanger Recycling system |
|||||
Raw materials and/or processes affected | Raw
materials affected : chrome Processes: Tanning |
|||||
% reduction in the waste flow | Reduction in chrome consumption:48% | |||||
Other waste flows affected | Reduction of nine times the chrome content in waste water and therefore in the treatment sludge generated. | |||||
Variation in production capacity | # | |||||
Others | # | |||||
Balance | Economic Viability | # | Material | Quantity | Unit cost | Total cost |
Saving | Chrome salt |
8,064 kg/year Quantity used previously: 16,800 kg |
0.72 €/kg | 5,806.08 €/year | ||
New costs | # | |||||
Total saving |
5,806.08
€/year
|
|||||
Investment | Equipment purchase | Heating module, made up of a 100,000 Kcal/h plate exchanger, + filter and recycling pump + controller, handling, temperature sensor + piping and accessories for recycling = (EUR 450.76 + EUR 3,005.06 + EUR 2,103.54 + EUR 3,005.06) x 2 drums ->EUR 17,128.84 | ||||
Service connection | # | |||||
Engineering | # | |||||
Others | # | |||||
Investment payback period | 17,128.84 / 5,806.08 = 2.95 years | |||||
Observations/other issues to be considered | There
is no saving in the treatment of waste water because the physiochemical
system used is not used exclusively for the treatment of water containing
chrome. This waste water only represent 6.5% of the total waste water generated.
Even though the chrome concentrations are very low, exactly the same conditions
need to be maintained for the production effluents to be correctly treated.
The sludge generated will have a lower chrome concentration. In the case of hazardous waste, this could mean that it would pass to the non-hazardous category and be landfilled, with the economic saving that this would entail. In this case, however, treatment sludge is considered to be Non-Hazardous Waste No special and therefore subsequent management would not be affected by any decrease in the chrome content. |
(1) Through the comparative analysis of the two systems, the following chrome ratio for 1,000 kg of pelt was observed: |
# | ||
ITEM
|
STANDARD
TAN
|
HIGH
EXHAUSTION TAN
|
Quantity
of chrome / pelt weight
|
25 kg
(2.5%)
|
13 kg
(1.3%)
|
Fixed
chrome
|
12 kg
(1.2%)
|
11.5
kg (1.15%)
|
Chrome
in the bath (recoverable)
|
7.6
kg (0.76%)
|
0.9
kg (0.09%)
|
Chrome
in the bath absorbed by the hide (unrecoverable)
|
5.4
kg (0.54%)
|
0.6
kg (0.06%)
|
For a given quantity of fixed chrome, the consumption diminishes almost to a half and the chrome content in the waste water is reduced 9 times, with an additional heat consumption of 50,000-60,000 Kcal. |
6.3.- Process modification - material substitution: |
use of chrome liquor |
The main objective of tanning
is to transform the hide, which is a decomposable (putrescible) substance
into a rot-proof (imputrescible) substance that is also resistant to the
action of enzymes. It is also to give the hide certain properties: homogeneity, feel, elasticity, etc, which are achieved by using one type of tanning or another and through the appropriate use of different factors (temperature, pH, basicity and masking). Chrome can be used in a solid form (powder) and in a chrome liquor liquid form. Powder is currently used and this is delivered in 25 kg bags with a basicity that is normally 35%. |
USE OF CHROME LIQUOR | ||||||
Proposal description | Objective: | Substitute chrome in powder form for liquid chrome in the tanning stage | ||||
Description |
The best available techniques
have been determined on the basis of the experience of the workers in
the company themselves and observations of the work method used in the
company. The grounds for applying this alternative are as follows: |
|||||
Technical feasibility | Technique | The advantages are highly significant yet difficult to quantify in economic terms because they are more qualitative than quantitative. | ||||
Equipment: | 12
m³ steam heated tank Piping with polyester insulation 2.7 m³/h impulsion pump Stainless steel recipient-316 with runners (1,000 litres) 1,100 l/h peristaltic pump |
|||||
Raw materials and/or processes affected | Processes: tanning | |||||
% reduction in the waste flow | Environmental
advantages through the significant improvement of working conditions. Reduction in the quantity of plastic bags and damaged pallets to be managed as waste. |
|||||
Other waste flows affected | # | |||||
Variation in production capacity | # | |||||
Others | # | |||||
Balance | Economic Viability | # | Material | Quantity | Unit cost | Total cost |
Saving | # | |||||
New costs | # | |||||
Total saving | ###### | |||||
Investment | Equipment purchase | 12
m³ steam heated tank + Piping with polyester insulation + 2.7 m³/h impulsion
pump + Stainless steel recipient-316 with runners (1,000 litres) + 1,100
l/h peristaltic pump = 7,512.65 € + 2,704.55 € + 793.34 € + 2,704.55 €+ 1,256.12 € = 14,971. 21 € |
||||
Service connection | # | |||||
Engineering | # | |||||
Others | # | |||||
Investment payback period | # | |||||
Observations/other issues to be considered | It is very important for the tank to be heated due to the extremes of temperature in the area where the factory is located. This will prevent the crystallisation of the chrome salts which could damage the hides. |
6.4.- Recycling and recovery: recycling of the pickling baths |
The picking operation, which follows the bating process, has several purposes: - It completes the deliming process as
it continues to eliminate the alkaline state of the hide to the point
where it becomes acid. The pollutants generated in pickling are the salt and acid added for the process and that remain in residual form in the water. The used pickling baths have a high concentration of sodium chloride, which is normally 8-10ºBe in the case of preservation pickles and 3-4ºBe in the case of conventional pickles. pH at the end of a preservation pickle should be between 1-1.5. |
RECYCLING THE USED PICKLING BATHS | ||||||
Proposal description | Objective: | Recycling the used pickling baths | ||||
Description | The used pickling baths have a high concentration of sodium chloride and they also contain by-products that could be reused in the following pickling operation (basically salt and acid). | |||||
Technical feasibility | Technique | The investment is very small in that it only requires a 5,000 litre-capacity tank that can stand the acid conditions and a pump to recycle the water to other pumps. | ||||
Equipment: | 5
m³ capacity plastic tank3 m 3/h DELASCO- type pump |
|||||
Raw materials and/or processes affected | Process affected : pickling | |||||
% reduction in the waste flow | Reduction
in water consumption: 70% recycling Reduction in the consumption of sodium chloride and sulphuric acid. |
|||||
Other waste flows affected | Prevent the disposal of effluents with a high salt concentration. | |||||
Variation in production capacity | # | |||||
Others | # | |||||
Balance | Economic Viability | # | Material | Quantity | Unit cost | Total cost |
Saving | Chemical products: acid and common salt | # | # | 601.01 €/year | ||
Water | Quantity
used before = 5m³/process x 100 process per year = 500 m³/year 70% x 500m³ = 350m³ |
1.53 €/m³ | 535.5 €/year | |||
New costs |
#
|
|||||
Total saving |
1,136.51
€/year
|
|||||
Investment | Equipment purchase | 5 m³ capacity plastic tank + 3 m³/h DELASCO- type pump = 1,803.04 EUR + 1,544.60 EUR = 3,347.64 EUR | ||||
service connection | # | |||||
Engineering | # | |||||
Others | # | |||||
Investment payback period | 3,347.64 / 1,136.51 = 2.9 years | |||||
Observations/other issues to be considered | 70% recycling is the maximum value determined for the production process to not be affected by waste water recycling and to maintain the quality of the product. |
7.- SUMMARY TABLE OF THE ALTERNATIVES |
SUMMARY TABLE OF THE ALTERNATIVES | ||||||
TYPE | OPPORTUNITY | ALTERNATIVE |
COST (EUR)
(guidance only)
|
INVESTMENT
PAYBACK PERIOD |
||
Source reduction | Change of technology | -
Saving in the consumption of chrome - Reduced pollution load (chrome) in waste effluents |
Hot chrome tanning |
17,128.84
|
2.94 years
|
|
Material substitution | -
Improved product quality - Improved workmanship - Improved environmental conditions (no dust or fumes in the air) |
Use of chrome liquor |
14,971.21
|
---
|
||
Recycling and recovery | Recycling of water | - Saving in water consumption for the production process | Recycling of the last rinse in the soaking operations |
6,611.13
|
1.6 years
|
|
- Saving in the consumption of water, sulphuric acid and sodium chloride- Decreased pollution load, mainly salts, in the effluents from the process. | Recycling of the pickling baths |
3,347.64
|
2.9 years
|