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.

Production (products)
Type of product
Lambskin
Goatskin
Annual production
2,500,000 feet2


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

The first step is the purchase of the hides, either as unworked raw leather or Wet Blue, by the company's specialist personnel.

Transportation of the hides from the place of origin to the factory

The next step is the transportation of the hides from the place of origin to the production facilities. In general, hides are usually delivered by lorries on wooden pallets, which provides for ease of unloading.

Delivery and storage

When the lorry loaded with hides arrives at the factory, the merchandise and papers are first cross-checked and the hides are then unloaded either into the unworked raw hide or Wet Blue storage location, according to the state of the hides being delivered.

The hides are adequately preserved here prior to beam house processing.

Test sampling


A test sample is made of a random number of hides in each batch that arrives in order to check that the conditions on arrival tally with the characteristics agreed to at the time of purchase.

Unusable parts removed


Once the test sample has been completed, the unusable parts of the hide are removed, such as heads, tails and rough hair. With hides that have been salted, this operation is done with a knife whereas an electric saw is used for dry hides.

Recounting and hides placed on the travelling carriage

Once the unusable parts are removed, the hides are counted and placed on the travelling carriage.

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

This consists of a series of successive paddle vat rinses with water and biocides to prevent any breakdown of the hide due to microorganisms.

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).
- Eliminate unwanted compounds, excreta, earth, blood, fleshings, urine, sweat, dust, micro-organisms and chemical products used for preservation.
- To eliminate salt. Salt on the inside of the hide is forced out due to the difference in saline concentration and the mechanical action.

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.

Removal of wool (or Painting)

There is still wool on the hides when they are removed from the paddle vat after the soaking operation. The following process is the removal of the wool, whereby a paint-like solution containing sulphur is applied on the flesh side of the hides and after a specified time the hide and wool can be separated.

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.

Liming

With the wool removed, the hides are loaded into the paddle vats for the liming operation.

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.
- Eliminate the epidermis with remains of hair and wool from the corium.

4 wooden drums with a 1:1 bath ratio (1 litre of water for each kilo of hide) are used for this.

Fleshing

Fleshing (or scudding) is a mechanical process that cleans the hide by eliminating subcutaneous tissue and adipose, which is where most of the fatty material in the hide is contained. Removing these in the initial stages of manufacture prepares the hide and enhances the penetration of chemical products applied in subsequent processes.

It is important for the hides not to be scored or marked; for this reason great care is needed when adjusting the machine.

Deliming

After the hides have been cleaned and most of the sulphur from the bath has been removed, they are delimed. The purpose of this is to achieve the right alkaline pH of the hide and prepare it for subsequent treatment by cleaning the pores of the hide and eliminating any alkaline remains mixed with collagen that can lead to swelling of the limed hide.

The equipment used for deliming is the same as that for liming, i.e., 4 wooden drums with a 100% bath ratio.

Bating (also known as drenching)

The hides are subjected to a bath with specific characteristics of temperature and pH and enzymes, which have the following effects, are added:
- They loosen and cause the peptisation of the structure of the collagen.
- They clean up the grain surface by eliminating remains of hair, epidermis, glands and fat.
- The hydrolysis of interfibrillar proteins.
- The breakdown of the elastin, reticulin, collagen and fats.

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, which follows the bating operation, is also applied in the same drum.

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.
If a preservation pickle is applied and the hides left for a specified time, the protoplasmal membrane of the fat deposits is attacked by the acid hydrolysis and breaks, forcing out the fat. This is a good time to carry out degreasing if this is necessary for the article.
- It also produces dehydration of the hide due to the combined action of the acid and salt.
- The acidification process prepares the hide for the subsequent mineral tanning process, leaving it positively charged, with counter ions in the corners and an overall neutral charge, which helps penetration.
- If pickling is not carried out, overtanning of the hide would occur in the following mineral tanning process due to the basicity of the tanning salt; given that the hide is anionic and the chrome cationic, the chrome would fix to the hide too quickly and in excess as a result of the charging.

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
- Fat efflorescence
- Difficulty in achieving good distribution and penetration of the products
- Uneven dyeing
- Reduced dye fastness
-
Non-adherent finishes.

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.

Tanning

The main objective of tanning is to covert the hide into a stable material which will not decay and make it resistant to hot water and the action of enzymes and micro-organisms.

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.

Roller pressing / Classification

Once the hide has been tanned and left for a specified time, it is passed through hydraulic machinery to remove the moisture (moisture content to 60-65%) and it is then taken to chrome storage and classified according to size, thickness and class. It is then stored prior to manufacture.

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

The hides are shaved by machine to make any further correction of the thickness of the hide and make it uniform.

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.

Retanning

A second tanning process is carried out to achieve optimum characteristics of homogenisation and porosity and to compact the structure. Synthetic chrome and phenol-based tanning products as well as vegetable tanning extracts are used in retanning, either individually or in combination. The treatment is carried out at a temperature of between 35-45ºC. No salt is used.

Fat-liquoring

The next process is fat-liquoring which gives the final softness and protection to the tanned hide which have been impaired during the previous processes. Through the use of fats and oils in appropriate mixes to lubricate and soften the fibre structure of the leather at a temperature of 55 to 60ºC, fat-liquoring gives it the required softness for the eventual end use.

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.

Dyeing

Dyeing involves colouring the hide according to eventual end use.

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.
The buffing machine consists of an emery wheel that makes two simultaneous movements, one circular movement on the axle and the other, an axial type movement, that prevents the formation of scratches or striations on the hide.

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.
Others types of hide are polished. This is achieved by fairly vigorous friction of the hide surface as it passes between cylinders that are under a certain pressure.

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:
- Conveyor belt.
- Measurement header.
- Automatic foot measurement marker.
- Foot measurement indicator and adder.

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:

Mechanical barscreen:

Water from the factory (from both the drums and paddle vats) flows into an outside channel approximately 50 cm wide, at the end of which there is a fixed rough-dressing grate with a 2 cm mesh. Particles larger than this size are retained by the grate and are periodically removed manually and managed as solid waste. Once the water has passed through the grate and prior to reaching the pump well, it passes through a tank (width 2m, height 3m and depth 2m), where the heavier colloidal particles separate out to the bottom, while that which floats goes into the pump well. This tank is cleaned periodically by a tank wagon.

Pump well:

Water from the mechanical barscreen and the separating tank falls by gravity into the pump well, which has an air activated agitator system although its sole function is to receive water which is then sent by mechanical pumping to the purification treatment process. The pump well has an approximate capacity of 50m³ and the surface is square-shaped although the lower part slopes down.

Grit Trap:

Water from the pump well is rough-dressed until particles larger than < 0,5 mm are separated out. The filter has two discs that turn and cause the filth to accumulate, which is very important for solids that it are difficult to eliminate using other filters, such as dust from buffing and reduced agents that are sometimes still present in the water. Solids that are removed are managed as solid waste whereas the filtered water falls by gravity to the homogeniser. If the filter cannot absorb all of the water forced through the pumps from the pump well, there is an overflow system that returns the water to the beginning again so that non-filtered water never enters the homogenisation tank.

Homogenisation:

The rough-dressed water enters the civil works circular homogenisation tank located outside of the separating tank. This tank is aired by way of a submerged current-type ventilator that is in constant operation and it also has a turbine that works intermittently, according to a timer.

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 coagulation-flocculation chamber is located next to the homogenisation tank and the water to be treated is pumped in at a constant rate. The quantity of water entering the separating tank is regulated and any water exceeding the set amount is returned to the homogeniser. The first product to be added is the coagulant, which is mixed in by the movement of the water whereas the flocculent, which is added straight after, needs to be mixed with a mechanical agitator that is located in the chamber itself.

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:

Once the chemical reaction has taken place, the water has to be separated from the flocculated material, and this operation is carried out in a brick-built separating tank with an inclined bottom that has a bridge scraper for the sludge. The separating tank covers an area of approximately 28m2.

The flushed water goes to the sewer system which leads to the municipal treatment plant while the sludge is pumped to the sludge thickener.

Sludge thickener and sludge preparation:

Sludge from the separating tank passes through a sludge thickener which increases the dry material content in the sludge and makes dehydration easier. The sludge thickener is located next to the homogeniser and a series of thin plates in installed to increase the separating capacity. The sludge passes through channels into an attached tank Ferric chloride is added according to the reading on a pH-metre and it finally goes into another tank where it is lime-adjusted. The quantity of lime added depends on the parameters entered in another pH-metre. It can occur that sludge is pumped from the separating tank and yet is not totally absorbed by the sludge thickener. In this case, it gets returned by an overflow and enters from the beginning again.

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:

Once the sludge has passed through the sludge thickener, it needs to be dehydrated because it is still very liquid. It is then pumped from the preparation chamber into the filter press.

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
** Estimated data


 

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:

• Steam boilers: Used to generate energy for different uses.

• 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
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
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
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
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.
*Estimated data



Sub Processes - Fleshing

The main waste produced is the fleshings extracted from the hide which are recovered externally.



ÉS
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
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
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
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
(1) Waste water has a high sodium chloride (8 to 10ºBe) and acid content and is therefore highly acid (pH 3 - 3.5 UpH).



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
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
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
(1) Waste water from the rinsing of chrome tanning, calculated as being 7m³/rinse, has a high concentration of chemical products with a pH of 3-4, high salinity, large amounts of chrome salts and leather fibres in suspension, and emulsified fat. This water is also given physiochemical treatment.



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
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
(1) Rinsing water from neutralisation, fat-liquoring and dyeing is slightly acid (pH 4-5) and mainly contains surfactants and, in some cases, emulsified surfactants, colouring matter/dyes, neutral salts and retanning agents. The volume of water from these operations varies considerably according to the article being manufactured.



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
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
•HOT CHROME TANNING
• USE OF CHROME LIQUOR
• RECIRCULATION OF THE PICKLING BATH



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.
Given the characteristics of the paddle vats and the bath ratios used in the production process, the volume of water used in beam house processes represents a significant proportion of the total amount of water consumed by the company.

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:
• Tanning with preprepared chrome liquor results in greater penetration with a better fineness of grain.
Improved workmanship. The worker does not have to handle 25-50 kg. bags.
• Improved environmental conditions. It is no longer necessary to handle chrome in powder form, which penetrates very rapidly into the respiratory tract due to the small size of particles. When the chromium salts are being prepared, a considerable quantity of green powder is found to frequently accumulate on the mucous membranes of the respiratory system, which is trivalent chromium salt.
The adding of chrome salt to the drum by means of a pump connected to the input tank stops the flow of the carriage that runs on gas-oil and the fumes in the air build up considerably over a period of a few hours.

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.
- It definitively stops the effect of bating.
- If a preservation pickle is done and the hide is then left for a time, the protoplasmic membrane of cells containing fatty material gets attacked by the acidic hydrolysis and breaks. This forces the fatty material out and facilitates the degreasing process.
- The hide also dehydrates.
- The hide is prepared for the following mineral tanning process.

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