Key Benefits:
Minister of Ecology and Sustainable Development,
In view of Regulation (EC) No 1774/2002 of the European Parliament and of the Council of 3 October 2002 laying down health rules applicable to by-products Animals not intended for human consumption;
In view of Commission Regulation (EC) No 808/2003 of 12 May 2003 amending Regulation (EC) No 1774/2002 of the European Parliament and of the Council laying down rules Health applicable to animal by-products not intended for human consumption;
In view of Council Directive 91 /271/EEC of 21 May 1991 on the treatment of urban waste water;
Given the environmental code, and In particular Article L. 512-5;
In view of the Labour Code, and in particular Article R. 231-53;
In view of Decree No. 53-578 of 20 May 1953 on the nomenclature of classified installations;
Given Decree No. 77-1133 of 21 September 1977 Modified for the purposes of the Act of 19 July 1976 on installations Classified;
In light of the Amended Decision of 23 January 1997 concerning the limitation of noises emitted to the environment by the classified installations;
In view of the Decision of 2 February 1998 as amended on water sampling and consumption Emissions of all types of facilities classified for the protection of the environment subject to authorization;
In the opinion of the Board of Governors of the facilities classified as of February 17, 2004,
Stop:
This Order lays down the requirements applicable to slaughterhouses of slaughter animals, poultry, rabbits and farmed game animals subject to Authorisation under heading 2210 of the classification of classified installations.
The provisions of this Decree shall apply to new and existing installations in accordance with the procedures laid down in Article 3 and in Chapter VI
In accordance with Article L. 512-5 of the Environment Code, the Prefectural Order for the authorisation of an installation may, as appropriate and under the conditions laid down in this Order, fix special provisions adapted to the Local circumstances.
For the purposes of this Order:
-installation: buildings in Which are carried out for the reception, waiting and slaughter of animals and for the cooling and storage of meat, including their annexes;
-annexes: buildings, hangars, areas and other reserved devices:
-storage of corpses, by-products and products not intended for human consumption, including leather;
-storage of waste (manure, manure, digestive tract contents);
-washing and parking of Transport vehicles for animals and meat;
-pretreatment and, where appropriate, treatment of effluent;
-handling, packaging and, where appropriate, processing of by-products whose destruction is not Not regulated by regulation;
-animals for slaughter: Animals belonging to bovine species (including species Babalus bubalus and Bison bison), porcine, ovine and caprine animals, as well as household solipeds;
-domestic poultry: birds belonging to the chicken species, turkeys, Pintades, ducks and geese;
game: wild animals raised and slaughtered as domestic animals: game birds, including ratites, ungulate game and rodents;
-specified risk material (SRM): Tissues of ruminants designated on the basis of the pathogenesis of subacute transmissible spongiform encephalopathies (ESST), as described in Article 31 (p) of the Decree of 17 March 1992 on the conditions to be met by the Slaughterhouses of slaughter animals for the production and placing on the market of fresh meat and determining the conditions for the sanitary inspection of such establishments;
-approval of composting plants, of biogas production, Incineration or processing: Approval within the meaning of Regulation (EC) No 1774/2004 referred to above.
The installation is established:
-at least 35 metres from wells and boreholes, other than those intended solely for the operation of the facility, sources, open-flow aqueducts, any underground or semi-buried installation used for the storage of water, The water is intended for drinking water supply or for the watering of vegetable crops, shorelines, stream banks;
-without prejudice to the hazard zones defined in the hazard study, 100 metres from homes Occupied by third parties or premises usually occupied by third parties (out of premises Occupied by staff related to the installation), approved stadiums or campgrounds, areas intended for habitation by urban planning documents against third parties, as well as bathing sites and beaches. This distance may be reduced for premises or annexes that do not pose a risk of nuisance to the neighbourhood, where the operator justifies compensatory measures implemented to prevent them or if the project's impact assessment Shows that the risks and nuisances are not increased.
In the case of the extension of existing installations, the provisions of this Article shall apply only to new buildings. They do not apply when these installations are brought into compliance.
Foreign persons at the facility Do not have free access to the installation. The whole installation, from which the animals are likely to escape, shall be closed and shall contain, as necessary, devices intended to prevent their escape from the installation.
The operator takes appropriate steps to integrate the installation into the landscape. The entire facility is maintained and maintained at all times.
The vicinity of the facility, under the control of the operator, is maintained and maintained in good condition. Discharge outfalls and their periphery are the subject of special care (planting, engazing, etc.).
The operator has sufficient reserves of products or consumables used on a routine or occasional basis to ensure environmental protection such as filters, neutralization products, inhibitory liquids, products Absorbents.
Operating procedures for the installation explicitly include controls to be performed in normal operation, following a shutdown for jobs Modification or maintenance of the facilities and the restoration of the facilities in the event of a serious incident or accident.
The operation shall be carried out under the direct or indirect supervision of a person named by the operator who A knowledge of the conduct of the facility and its hazards; and Disadvantages.
Without prejudice to the provisions of the Labour Code, instructions are established, kept up to date and brought to the attention of staff in the places frequented by the staff. These instructions specify:
-procedures for the emergency and safety of the facility, including the slaughter line and effluent treatment facilities;
-measures to be taken in the event of a leak on a container or pipeline Containing dangerous or polluting substances such as ammonia or blood collected.
When a tower (s) Aerorefrigerators (1) or humidifier are directly associated with Installation, the operator must comply with the following provisions:
I.-The operator shall ensure the presence and effectiveness of a droplet, or " Blister, so as to limit the emission of water droplets by the aero-frigerated tower.
II-1. The operator shall maintain and maintain appropriate maintenance and maintenance in order to limit the proliferation of legionelles in the system and their emission. The operator shall ensure that the surface and the lining and the peripheral parts (droplet, caisson ...) are kept in good condition for the duration of the aero-frigerated tower.
II-2. Prior to the reactivation of the cooling system after a prolonged shutdown, and at least once a year, the operator shall make the following minima to:
-an aerofrigerated tower tray flushing;
-a drain of the water circuits in the aerorefrigerant tower as well as extra water circuits;
-a mechanical and/or chemical cleaning of the water circuits, garages and Peripheral parts;
-disinfection by a product whose effectiveness in disposing of legionella has been recognized, such as chlorine or any other disinfectant with equivalent safeguards.
If the operator warrants Failure to complete the emptying of the circuits, it must implement a Effective treatment against legionella proliferation.
In all cases, a water analysis for legionella research must be conducted within 15 days of the restart of the aero-frigerated tower.
II-3. The operator shall carry forward in a follow-up workbook all the operations carried out and will keep this notebook available for inspection of the classified installations. This notebook includes:
-a diagram of the installation that includes a description of the tower and tracking of the dead arms;
-the volumes consumed monthly;
-the shutdown and operating periods;
-the Operations carried out (drain, cleaning, water treatment, etc.);
-sampling and analysis performed.
III. -Without prejudice to the provisions of the Labour Code, the operator shall make available to staff involved in the vicinity of the cooling system or on the system itself suitable personal protective equipment (aerosol masks) Solids and liquids, gloves ...) intended to protect them from exposure to chemicals and aerosols that may contain pathogens.
A panel must report the wearing of the required mask.
IV. -The inspection of classified installations may at any time request the operator to carry out samples and analyses in order to assess the efficiency of the maintenance and maintenance of the water circuits connected with the operation of the system Cooling. These samples and analyses are carried out by a qualified laboratory whose choice is subject to the inspection of classified installations. The costs of sampling and testing are borne by the operator.
V.-Water analyses for legionella research are carried out during the period of operation of the aero-frigerated tower (s), at least once a year before Summer.
An annual summary of results and analyses is sent to the inspection of classified installations.
VI. -If the water analyses for legionella research show a concentration greater than 100 000 colony-forming units per litre of water (UFC/l), the operator shall immediately stop the operation of the cooling system, in Immediately inform the inspection of the classified installations and propose appropriate corrective actions.
If the water analyses indicate a concentration between 1000 and 100 000 UFC/l, the operator will have to implement The measures necessary to reduce the concentration by legionels in Below 1000 CFU/l. It will carry out a new control two weeks after the collection having highlighted the concentration between 1 000 and 100 000 UFC/l. Control will be renewed every two weeks as long as this concentration remains between these two values.
VII. -All results of water analyses for legionella research greater than 1 000 UFC/l (points II, VI and V) shall be sent as soon as they are received at the inspection of classified
. -The make-up water supply of each cooling system responds to the rules of the art and is equipped with a meter.
The cooling system's water supply system is equipped with a set of disconnection protection located Upstream of any treatment of water, in the case where the system is fed by the public water distribution network for consumption. Aerosol releases are not located at the right of an air intake or the right of opening. The discharge points shall also be arranged in such a way as to avoid the siphoning of droplet air in the ventilation ducts of nearby buildings or the inner yards.
Electrical installations are carried out, maintained and controlled in accordance with the regulations in force. Monitoring reports are made available to inspectors of classified installations.
The installation is effectively protected against the risks associated with the effects of static electricity and lightning.
Without prejudice to the provisions of the Labour Code, the buildings and annexes are designed and arranged in such a way as to prevent the propagation effectively Fire, to allow for the evacuation of persons and The rapid response of emergency services.
The facility is equipped with fire fighting capabilities appropriate to the risks involved. Special attention is paid to the premises where the refrigeration plant is located. In sufficient numbers, these means are properly allocated on the area to be protected. The means of fighting and preventing fire are fixed by the prefectural order.
Buildings and annexes are kept clean and regularly cleaned so as to avoid piles of combustible materials and dust.
The premises are equipped in high part with devices for the evacuation of smoke and flue gas from fire. Manual opening commands are placed near access. The de-enfuming system is adapted to the specific risks of the installation.
For Flow Determination, the And, to the extent possible, diffuse emissions are taken into account
The operator shall make all arrangements Necessary in the design, construction and operation of the facility to prevent the risk of accidental pollution of air, water or soil.
In the event of accidental pollution caused by the establishment, the operator Provides, as soon as possible, all known information It provides for the determination of the safeguard measures to be taken in relation to persons, fauna, flora and works exposed to this pollution.
Aqueous effluents recovered, likely to be polluted (pumping, washing Of installatoin, etc.) are stored before their recovery or disposal, under conditions that do not pose a risk of pollution.
Any accident or incident that might cause Infringement of the interests referred to in Article L. 511-1 of the Environment Code shall be declared, as soon as possible, to the inspection of classified installations and shall be recorded in the form of a written record (origin and causes of the Phenomenon, consequences, measures taken to prevent it and to prevent it from recurring ...) transmitted within 15 days to the inspection of classified installations.
The collection system is a separative network for isolating polluted waste water from water Unlikely to be polluted.
Devices are used to insulate waters that may be polluted in an accident or fire, including water used for the extinguishing of a disaster, water drainage systems Runoff. A notice sets out the arrangements for the implementation of these devices and the treatment of these polluted waters
The cleaning and disinfecting area of vehicles used in the transport of animals is designed to To recover from each use all the effluents produced and to direct them to the pretreatment plant of the establishment or to the manure storage structures.
The premises for holding and slaughtering animals, Cooling and storage of carcasses and storage of by-products Of animal origin are constructed of impermeable, shock-resistant materials, easy to clean and disinfect on all their height.
The soil is watertight, resistant to the passage of equipment for handling stored products And designed to facilitate the flow of drip juices, residual dripping blood and cleaning water to collection facilities.
Animal blood collection is carried out in a manner that minimally reduces the need for Controllable flow to effluent collection facilities.
In ruminant slaughterhouses, locations on which removal, handling and/or sampling are carried out Specified risk material shall be designed in such a way as to avoid or, failing that, limit the flows from such products and their dispersion to the ground, in particular by the rational use of water and a collection at the Source of possible residuals of these materials
I. -Any storage of a liquid capable of creating water or soil pollution is associated with a holding capacity whose volume is at least equal to the greater of the following two values:
100 % of the capacity of the largest reservoir ;
50 % of the total capacity of the associated tanks.
For storage of containers of unit capacity less than or equal to 250 litres, the holding capacity is at least equal to:
-in the case of flammable liquids, with the exception of lubricants, 50 % of total barrels capacity;
-in other cases, 20 % of total barrels capacity;
-in all cases 800 litres minimum or equal to total capacity When it is less than 800 litres.
II. -The holding capacity is impervious to products that it may contain and resists the physical and chemical action of fluids. The same shall apply to its sealing device which is kept closed under normal conditions.
The sealing of the associated reservoir (s) can be checked at any time.
The products recovered in the event of an accident shall be rejected only Under conditions that are in accordance with this Order or are disposed of as waste.
Tanks or receptacles containing incompatible products are not associated with the same retention.
Storage of flammable liquids, as well as Other products, toxic, corrosive or hazardous to the environment, Is permitted below ground level only in storage tanks, or assimilated tanks, and for flammable liquids, under the above conditions.
The operator has the documentation to know the nature and risks of the hazardous products present in the facility, in particular the data sheets of Article R. 231-53 of the Labour Code. Drums, tanks and other packaging shall bear in very legible characters the names of the products and the hazard symbols according to the regulations in force.
Waste and fermentable animal by-products, including those recovered upstream of the screening, are stored in suitable premises or devices to avoid odours, Contact with and access to stormwater by other animals.
During storage and at the time of removal of these wastes and byproducts, and in particular in ruminant slaughterhouses removing SRM, the flow juices are directed to the effluent pretreatment facility Slaughterhouse.
The waters resulting from the cleaning of premises and storage devices for waste and by-products (bacs having contained meat and meat offal and, in ruminant slaughterhouses, SRM) are collected and directed to The installation of pretreatment of the effluent from the abattoir.
Dead bodies, wastes, and Fermentable by-products not intended for human consumption are removed or treated at the end of each work day if stored at room temperature. Storage of more than 24 hours shall be carried out in premises or devices ensuring their containment, if necessary refrigerated.
The area reserved for manures and stercorals shall be implanted so as not to interfere with the vicinity. It is weathered and insulated in order to recover the dripping juices to direct them to the pretreatment plant of the establishment or the manure storage structures.
With the exception of anaerobic treatment processes, The development of anaerobic conditions in storage or treatment basins or in open channels is avoided in all circumstances. These installations are equipped with aeration devices and/or covered, if necessary
Facilities are designed and operated to limit unnecessary use of water. The maximum level of consumption associated with slaughter operations in no way exceeds the value of 6 litres of water per kilogram of carcass. Where the refrigeration of carcasses is ensured by immersion, the level of consumption shall not exceed 10 litres of water/kg of carcass.
In the case of a drinking water supply by a public network, the work is equipped with a disconnection device. The volumes of water used are measured by the meter equipped with the connection of the facility.
Works
they are to be constructed in the bed of a watercourse, they shall respect, without prejudice to any authorization that may be required under Article L. 432-3 of the Environment Code, the provisions of articles L. 432-5 and L. 432-6 of the said code.
Their implementation and operation are consistent with the provisions of the water management and management plan and the water management and management scheme when it exists.
When drilling in the slick, all provisions are made to avoid communication of slicks Separate water, unless explicitly authorized in the authorization order, and To prevent the introduction of surface pollution.
In the event of cessation of use of drilling, the operator shall take appropriate measures for the sealing or sealing of the drilling in order to avoid pollution of the water bodies The
of a new drilling or the decommissioning of a drill is carried out prior to the prefect's knowledge with all the hydrogeological impact assessment elements.
Water collection structures, referred to in sections 22 and 23 above, are equipped with a totalizer measuring device. This device shall be recorded daily if the flow rate is likely to exceed 100 m³ /d, weekly if the flow rate is lower. The results, recorded in a computerized register, shall be kept at the disposal of the inspection of installations classified for a period defined in the authorization order
Effluents:
-the waters resulting from the activity (process, washing);
-the valve (sanitary) waters.
The transmission lines are adapted to the nature of the effluent that they are likely to contain. They are properly maintained and are subject to appropriate periodic reviews to ensure that they are in good condition. The operator identifies the pipes that require regular curing, proposes a curing schedule and provides for the disposal of these curing sludges.
The different pipes are located according to the rules in Effective.
A schematic of all networks and a sewer plan are established by the operator and regularly updated. They shall be kept at the disposal of the inspection of classified installations as well as fire and rescue services.
With the exception of accidental cases where the safety of persons or installations is compromised, it is prohibited to establish Direct links between the effluent collection systems to be treated or destroyed, and the receiving environment.
The installation has a preprocessing device Effluent containing, at a minimum, a screening and, where applicable, screening, descaling and degreasing. The reduction shall be equipped with openings or mesh size not exceeding 6 mm or equivalent systems ensuring that the size of the solid particles of the waste water passing through these systems does not exceed 6 mm. Any grinding, maceration or other process that can facilitate the passage of animal material beyond the pre-treatment stage is excluded. This device is designed to cope with variations in the flow, temperature, or composition of the effluent to be treated, in particular during the start-up or shutdown of the facilities.
The type of relief used, the time of the Stay of the effluents stored and the frequency of maintenance of these devices are adapted accordingly.
Pre-treatment facilities are properly maintained. They are equipped with devices for sampling discharges and measurements of their discharge in good conditions.
If an outage is likely to lead to an exceedance of the imposed limit values, the operator Takes the necessary steps to reduce the pollution emitted by reducing or stopping the operations concerned.
Effluents should not contain harmful substances in sufficient quantities to inhibit the biological process Scrubbing devices.
Waste water discharged to the natural environment meets the concentration or yield limit values specified in Appendix I of this Order.
The limit values for discharge are consistent with the quality objectives and the fishing vocation of the receiving environment, the provisions of the master plan for the development and management of water and the water management and management scheme, When it exists.
For this purpose, the authorization order can fix multiple Limit values according to stream flow rate, dissolved oxygen level, or any other significant parameter.
Rejection points in the natural environment are as small as possible while taking into account the conditions of the Dilution in the natural environment during periods of drawing. Release structures allow for good diffusion of effluent to the receiving environment.
The authorization order sets the maximum daily flow rate for the (or) rejection (s).
In the event that the facility does not have its own treatment devices, the operator shall ensure that the treatment of its effluent by a treatment plant is hazardous External to the installation. It ensures compliance with discharge limit values compatible with the treatment plant's treatment capabilities and the discharge limit values of this station.
Connecting to a collective, urban or municipal sewage treatment plant Can only be considered if the collective sanitation infrastructure (network and treatment plant) is capable of delivering and treating the effluent in good conditions.
The impact study has a specific component Relating to connection. This component attests to the capacity of the plant to treat the effluent as described above, determines the characteristics of the effluent that may be allowed on the network, and specifies the nature and size of the pretreatment works Where appropriate, to reduce source pollution and to minimize or regulate pollution fluxes and connected flows. The effects of the connection on the operation of the station, the quality of the sludge, and where applicable, their recovery, are in particular considered in the light of the possible presence of mineral or organic micropollutants in the Effluent.
When the maximum flux of effluent is likely to exceed 15 kg/day of MEST, 15 kg/d of DBO5 or 45 kg/d of COD, the concentration limit values calculated on the basis of a water consumption consistent with that indicated in Section 20 imposed on the effluent at the exit of the facility before connecting to a station The following values:
MEST: 600 mg/l;
DBO5: 800 mg/l;
COD: 2000 mg/l;
Global nitrogen (expressed in N): 150 mg/l;
Total phosphorus (expressed in P: 50 mg/l.
The authorization order may prescribe upper limit values, in particular depending on the consumption of water per kilogram of carcass, and whether the impact study demonstrates, based on an argument of nature And, where appropriate, economic, that such provisions may be adopted without resulting in any lesser guarantee vis-de-vis the requirements for the proper functioning of the urban treatment plant and the protection of The environment.
For pollutants other than those regulated above, The limit values are the same as for a rejection in the natural environment.
The requirements of the authorisation order issued under the legislation of the classified installations shall apply without prejudice to the authorisation of the connection to the Public network issued, pursuant to Article L. 1331-10 of the Public Health Code, by the community to which the network belongs.
For installations already connected with an extension, the impact assessment shall include a Specific part relating to connection. This component attests to the suitability of the sanitation infrastructure to carry and treat the effluent from the slaughterhouse in good conditions, determines the characteristics of the effluent that can be admitted to the system, and specifies the nature of the effluent. The dimensioning of planned preprocessing works, if any, to reduce source pollution and minimize pollution fluxes and flows
All provisions are made to limit the amount of waste Products, in particular by carrying out all possible and economically acceptable recovery operations.
Wastes which cannot be recovered shall be disposed of in installations entitled to receive them under fixed conditions By the regulations in force, in particular as regards Removal of SRM and animal by-products.
Animal by-products of the facility are stored under no risk conditions (prevention of flight, runoff, infiltrations into the soil, Smell ...) for the surrounding, human and animal populations, and the environment. They shall be disposed of or valued in accordance with the regulations in force.
Disposable materials and tools used that may be soiled by specified risk material shall be disposed of in accordance with Decree No. 97-1048 of 6 November 1997 on the disposal of waste from infectious and assimilated risk-care activities and anatomical parts and modifying the public health code.
Materials Collected during the pre-treatment of the effluent from the facility defined in Article 26 of this Order and the curing sludge from the pipes upstream of this pretreatment shall be collected, transported and disposed of in accordance with the Regulation (EC) No 1774/2002 mentioned above
Without prejudice to restrictions defined by regulation on health grounds, may be the subject of Land application on or on agricultural land:
-the effluents, excluding the valves, that have undergone the pre-treatment set out in section 26 of this Order when the operator does not have a treatment plant;
-the sludge produced and recovered in the devices Scrubbers located downstream of the relief defined in section 26 of this Order;
-the manure, with or without litter, whether or not processed, and the contents of the digestive system separated from the digestive system in accordance with the regulations Effective.
Not subject to application of subproducts of Unprocessed slaughter, including blood and materials recovered upstream of the pre-treatment set out in section 26 of this Order. These are the waste stopped by the roasted soil siphons located in the working premises, the discharge waste, the curing sludge from the pipes upstream of this pretreatment and the raw waste of degreasing
For ruminant slaughterhouses, these materials are subject to destruction by incineration or co-incineration. In other cases, these materials may be valued at authorized installations in accordance with the regulations in force.
The applications shall be subject to a preliminary study included in the impact assessment and shall comply with the provisions of the The decree of 17 August 1998 amending the decree of 2 February 1998 on water sampling and consumption, as well as emissions of all kinds of installations classified for the protection of the environment subject to authorisation.
The operator is implementing an emissions monitoring program for the facility. The measures shall be carried out under its responsibility and at its own expense. The authorization decree sets out the nature and frequency of the measures defining the monitoring programme in accordance with the articles below. Depending on the characteristics of the facility or the sensitivity of the environment, other pollutants may be targeted or lower thresholds can be defined.
The methods used are the reference methods indicated in Annex II. However, the authorization order may include other methods where the results obtained are equivalent to those provided by the reference methods.
At least once a year, the measures are carried out by a chosen body. With the inspection of installations classified under conditions of triggering defined with it.
The results of all measurements shall be transmitted to the inspection of installations classified according to a frequency defined in the order Prefectural. They shall be accompanied by written comments on the possible causes of exceedance, as well as on the corrective actions implemented or envisaged.
Without prejudice to the third paragraph of this Article, the inspection of Classified facilities may, at any time, collect liquid or gaseous effluent, waste or soil effluent and perform sound level measurements.
The cost of sampling and testing is borne by the operator.
The operator is implementing an effluent monitoring program that is released or connected. The frequency of measurement of the parameters Debit, DCO, DBO5 and MEST is consistent with that indicated in Appendix III.
When the installation is connected to a collective treatment plant, a minimum monthly measurement is performed on the total nitrogen and the Total phosphorus.
When the facility has its own wastewater treatment devices and when authorized daily flows exceed the values shown below, a daily measurement is performed on total nitrogen and total phosphorus.
Total Nitrogen: 50 kg/day.
Total phosphorus: 15 kg/day.
These measurements are made from a sample taken over a 24-hour period in proportion to the flow rate.
In the case of discharges from lagoons, thresholds, or Different frequencies can be fixed for the MEST parameter. Where the exceedance results in a majority of the flow from the natural environment, the order provided for in Article 32 may set a lower frequency.
If the installation has one or more emissaries of off-gases, the operator shall, within three months of notification of the authorization order, make a measure of the hourly rate of emission of the Releases to the atmosphere and hourly dust, dioxide, and Sulphur and nitrogen oxide. The result shall be forwarded to the Prefect, who shall decide, where appropriate, for the establishment of a regular monitoring programme for gaseous releases and corrective measures.
Installation sound emissions comply with the provisions of the above order of 23 January 1997.
Installation is Constructed, equipped and operated in such a way that its operation cannot be the source of mechanical vibrations that could compromise the health or safety of the neighbourhood or constitute a nuisance to it.
Facilities authorizations are compatible, for the water domain, with the provisions of the master plan The development and management of water and, where appropriate, the water management scheme When it exists.
The provisions of this Order apply to installations for which the authorization order Will intervene more than four months after the publication of this Order in the Official Gazette of the French Republic, as well as amendments to existing installations requiring a new application subsequent to that date Authorisation in accordance with the combined provisions of Articles L. 512-15 Of the Environmental Code and 20 of Decree No. 77-1133 of 21 September 1977, as well as the extensions of the existing installations.
This Order shall apply to existing installations within one year of its publication in the Official Journal of the French Republic.
The requirements to which existing installations are already subject shall remain applicable until the entry into force of these provisions.
For the provisions of Article 35 concerning Noise, application procedures to new facilities, and Are those of the Order of January 23, 1997.
The Director of Pollution Prevention and Risk is responsible for the execution of this Order, which will be published in the Official Journal of the French Republic.
A N N E X E I
WATER POLLUTION SUPERFICIENT
When the maximum allowable daily flow exceeds the tenth of the interannual average flow within the meaning of Article L. 232-5 of the rural code of the watercourse or if it is greater than 100 m³ /day, the order of fixed authorization Also a limit to the monthly average daily rate and a value Instantaneous limit.
The temperature of the effluent discharged must be less than 30 ° C and the pH must be between 5.5 and 8.5, 9.5 if there is alkaline neutralization.
The colour change of the receiving environment, measured in one point Representative of the mixing zone, shall not exceed 100 mg Pt/l. After establishing a correlation with the method using platinum-cobalt control solutions, the color modification may, as necessary, also be determined from the optical densities measured at three wavelengths At least, spread over the entire visible spectrum and corresponding to maximum absorption zones.
For the receiving waters to which the provisions of Decree No. 91-1283 of 19 December 1991 apply, the effects of the discharge, as measured in The same conditions as before, must also respect the The following provisions:
-do not cause a maximum temperature rise of 1.5 ° C for salmon waters, 3 ° C for cyprinicolous waters and 2 ° C for shellfish waters;
-not induce a temperature greater than 21.5 ° C for water Salmon, at 28 ° C for cyprinicolous waters and at 25 ° C for water for the production of food water;
-maintain a pH between 6 and 9 for salmon and cyprinid waters and for bathing water, including between 6.5 And 8.5 for water intended for the production of food water, and between 7 and 9 for water Shellfish;
-do not result in an increase of more than 30 % of the suspended matter and a variation greater than 10 % of the salinity for the shellfish waters.
On a daily average sample and in accordance with the provisions Of section 27, the waste water discharged to the natural environment meets either the concentration limit values or the performance limit values defined in the table below:
You can view the table in OJ
No 141, 19/06/2004 text number 40
On the other hand, the specific pollution flow calculated, unless otherwise specified, from a Daily production must not exceed:
You can consult the table in OJ
No. 141 of 19/06/2004 text number 40
Specific pollutants: before discharge into the natural environment or In an urban collective sanitation network:
-total hydrocarbons (NFT 90-114): 10 mg/l if the flux is greater than 100 g/d.
Nitrogen and phosphorus fluxes comply with the following provisions:
(a) General:
-Nitrogen (global nitrogen including organic nitrogen) Ammonia nitrogen, oxidized nitrogen): 30 mg/l in monthly mean concentration when the maximum daily flow allowed is equal to or greater than 50 kg/d.
Different concentration limit values may be set by the authorization order when the performance of the Installation treatment plant reaches at least 80 % for nitrogen for new installations and 70 % for modified installations.
-Phosphorus (total phosphorus):
10 mg/l in monthly mean concentration when the maximum daily flow allowed is equal to or greater than 15 kg/d.
Different concentration limit values may be set by the authorization order when the performance of the Installation treatment plant reaches at least 90 % for phosphorus.
(b) Special provisions for releases to the natural environment belonging to a eutrophication sensitive area as defined under Article 6 of the Decree No. 94-469 of 3 June 1994 on the collection and treatment of water Waste referred to in Articles L. 2224-8 and L. 2224-10 of the General Code of Territorial Communities.
In addition to the preceding provisions, the authorisation order, according to the levels of flow of the discharge, the characteristics of the receiving environment and The eutrophication-sensitive zone requirements impose the following provisions for at least one of the two parameters according to the receiving environment:
-Nitrogen (global nitrogen including organic nitrogen, ammonium nitrogen, Oxidized nitrogen):
15 mg/l in monthly mean concentration when the maximum daily flow allowed is equal to or greater than 150 kg/day;
10 mg/l in monthly mean concentration when the maximum daily flow allowed is equal to or greater than 300 Kg/d.
Different concentration limit values may be set by the authorization order when the facility's performance at the facility reaches at least 80 % for nitrogen.
-Phosphorus (total phosphorus):
2 mg/l in monthly mean concentration when the maximum daily flow allowed equals or exceeds 40 kg/d;
1 mg/l in monthly mean concentration when the maximum daily flow allowed is greater than 80 kg/day.
Des Different concentration limit values may be set by the authorization order when the performance of the installation treatment plant reaches at least 90 % for phosphorus.
For nitrogen, when the treatment process is carried out Is a biological process, the provisions of a and a b are Met when the water temperature at the reactor level is at least 12 °C. This temperature condition can be replaced by the determination of due periods as a function of regional climatic conditions.
For nitrogen and phosphorus, the average concentration on a 24-hour sampling Exceeds twice the limit values set to a and b.
A N N E X E I I
REFERENCE METHODS
The following list contains the main reference methods approved and Experimental methods to which this order refers. Possibly, the analysis of some parameters may require the use of methods not explicitly referred to below. In case of modification of the standard methods, the new provisions shall apply within six months of publication.
For Waters:
You can consult the table in OJ
No 141, 19/06/2004 text number 40
You can view the table in the OJ
n ° 141 of 19/06/2004 text number 40
The method of quantitation Kjeldahl allows to measure the Non-oxidized nitrogen compounds. Global nitrogen is the sum of the nitrogen measured by the Kjeldahl method and the nitrogen contained in nitrites and nitrates.
For gases: emissions from stationary sources:
You can view the table in the JO
n ° 141 of 19/06/2004 text number 40
For soil:
You can view the table in OJ
No. 141, 19/06/2004 text number 40
For sludge:
You can view the table in OJ
n ° 141, 19/06/2004 text number 40
A N N E X E I I I
MONITORING OF EFFLUENTS
Frequency of measurements (number of days per year)
Gross organic pollution load received by the treatment plant expressed in kg per day:
You can view the table in OJ
No. 141 of 19/06/2004 text number 40
The gross organic pollution charge is calculated in DBO5 on the basis of load Average daily of the week in which the highest load of polluting substances is produced in the year (Art. R. 2224-6 of the TMC).
Done at Paris, April 30, 2004.
For the Minister and by delegation:
The Director of the
Pollution Prevention and Control Risks,
delegate to major risks,
T Found
