Key Benefits:
Publics concerned: operators of facilities classified for environmental protection (ICPE) under the registration regime under section 2410 of the ICPE nomenclature (installation where wood or similar fuel materials are used).
Subject: creation of general requirements for facilities under the registration regime under heading 2410.
Entry into force: the text comes into force on the day after its publication.
Notice: This Order sets out the technical rules that must be implemented by ICE operators under the registration regime under section 2410 to prevent and reduce the risk of accidents or pollution.
References: This text can be accessed on the Legifrance website ( http://legifrance.gouv.fr).
Minister of Ecology, Sustainable Development and Energy,
Considering Regulation No. 1272/2008/EC of the European Parliament and of the Council of 16 December 2008 on the classification, labelling and packaging of substances and mixtures, amending and repealing Directives 67/548/EEC and 1999/45/EC and amending Regulation (EC) No. 1907/2006;
In light of Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000, establishing a framework for community water policy;
Vu le environmental codeArticles L. 211-1, L. 220-1, L. 511-2, L. 512-7, D. 211-10, D. 211-11 and R. 211-94;
Vu le Decree No. 96-1010 of 19 November 1996 for devices and protection systems intended for use in explosive atmospheres;
Considering the decision of 20 April 1994 on the declaration, classification, packaging and labelling of substances;
Considering the decision of 23 January 1997 on the limitation of noises emitted in the environment by facilities classified for environmental protection;
Considering the amended decision of 21 November 2002 on the reaction to fire of construction and development products;
Considering the 14 February 2003 decision on the performance of roofs and roof coverings exposed to an outdoor fire;
Considering the amended Decree of 22 March 2004 on fire resistance of products, construction elements and works;
Considering the decision of 31 January 2008 on the register and annual reporting of pollutant emissions and wastes;
In view of the July 7, 2009 Decision on Air and Water Analysis Procedures in CEPAs and Reference Standards;
Considering the 17 July 2009 decision on measures to prevent or limit the introduction of pollutants into groundwater;
In view of the decision of 4 October 2010 on accidental risk prevention in licensed facilities classified for environmental protection;
Considering the opinion of the professional organizations concerned;
Based on the comments made at the public consultation held from 27 February 2014 to 20 March 2014, pursuant to theArticle L. 120-1 of the Environmental Code ;
In light of the opinion of the Higher Council for the Prevention of Technology Risk of 25 March 2014,
Stop it!
This Order sets out the requirements for classified facilities under heading 2410. It does not apply to existing facilities already authorized under heading 2410.
These provisions apply without prejudice:
- special requirements which may be accompanied by the registration order in the conditions fixed by the articles L. 512-7-3 and L. 512-7-5 the environmental code;
- other legislation, plans and other approved guidance and planning documents.
Definitions. For the purpose of this Order, the following means:
"Green wood": non-dried wood with a minimum of 30% moisture defined by the ratio (water mass/dried wood mass) and expressed in %.
"First processing of wood": cutting of round wood by sawing, rolling, cutting or crushing.
"Second processing of wood": complementary machining, assembly, processing or finishing operations using the products from the first processing of wood.
"Spandage": any application of waste or effluent on or in agricultural soils.
"Emergence": the difference between the level of continuous pressure weighted A of ambient noise (operating installation) and residual noise (in the absence of the noise generated by the installation).
"Events": normalized surfaces, burst pressure in case of known explosion (the material and surface of the vent are fixed by the manufacturer, according to dimensioning standards and construction standards, to lead to a certain burst pressure; This type of surface is often encountered on dust filters for example). The vent must remain in solidarity with the walls on which it is attached and not fragment.
"Related products": wood drops or residues (can come from the first or second processing.
"Polverent product": product that is in the form of light powder, floury product. Any product made up of more than 20% particles with a diameter of not more than 100 mm is considered pulverulent.
"closed structure": closed structure over 100% of its perimeter.
"Sufflable surfaces": surfaces that can be elements of the volume more fragile than the structure of it and relatively low burst pressure (vitres, bardages...).
"Aspiration system": A system of suction of saws and shavings includes capturing devices on the machines, a network of transport of captivated sawdusts and shavings, a unit of suction-deep intended to filter the polluted air, a system of introduction of new air to compensate, either in whole or in part, the volumes of air extracted by the installation of aspiration and a place of storage
"Mezzanine": height surface that occupies not more than 50% of the surface of the lower cell level and does not have a closed space. Beyond this limit, the surface is considered a level.
"Level": surface of the same floor available for storage or other activity.
"biogenic VOCs": VOCs that are produced by living organisms.
"Regulated Areas of Emergence":
- the interior of the buildings inhabited or occupied by third parties, existing on the date of the filing of the registration file, and their closest external parts (course, garden, terrace) excluding those of the buildings located in the areas intended to receive artisanal or industrial activities;
- the building areas defined by urban planning documents that are opposable to third parties and published on the date of the filing of records;
- the interior of buildings inhabited or occupied by third parties that have been established after the date of the filing of records in the building areas defined above, and their closest external parts (course, garden, terrace), excluding those of buildings located in areas intended to receive artisanal or industrial activities.
The facility is established, completed and operated in accordance with the plans and other documents attached to the application for registration.
The operator shall enumerate and justify, as appropriate, all arrangements for the design, construction and operation of the facilities to comply with the requirements of this Order.
The operator shall prepare and maintain a record with the following documents:
- a copy of the application for registration and the accompanying file;
- the record record maintained and dated according to the modifications made to the facility;
- the registration order issued by the prefect and any prefectural order relating to the installation;
- results of effluent and noise measurements over the past five years;
- the registry of all reports of accidents or incidents made at the inspection of classified facilities;
- the various documents provided for in this Order:
- the risk location plan (cf. art. 8);
- the register indicating the nature and quantity of dangerous products held (cf. art. 9);
- the general plan of storage (cf. art. 9);
- the safety data sheets of the products present in the installation (cf. art. 9);
- the register indicating the cleaning dates (cf. art. 10);
- supporting evidence of fire resistance properties of at-risk premises (cf. art. 11);
- operating instructions (cf. art. 25);
- the register(s) of periodic check(s) and maintenance of equipment (cf. art. 14, 17 and 20);
- register of industrial water sampling results (see article 28);
- the effluent collection network plan (cf. art. 29);
- the waste register (cf. art. 51);
- the emission monitoring programme (see art. 52).
This file is subject to inspection of classified facilities.
The facility is located at a minimum distance of 10 metres from the property limits.
The facility is not above or below premises inhabited or occupied by third parties.
Without prejudice to urban planning regulations, the operator shall adopt the following provisions, necessary to prevent theft of dust and other materials:
- the roadways and parking areas of the vehicles are fitted (gradient forms, coating, etc.) and properly cleaned;
- vehicles leaving the facility do not cause dust or mud to be deposited on the traffic lanes. For this purpose provisions such as the washing of the wheels of the vehicles are provided if necessary;
- in the vicinity of the installation, if possible, the surfaces are grassed or vegetated and vegetation screens set up.
The operator shall make appropriate arrangements to integrate the installation into the landscape.
The entire installation is maintained clean and maintained permanently.
The premises of the facility, under the control of the operator, are designed and maintained in good condition of cleanliness. Release emissaries and their periphery are the subject of special care.
The operator shall identify, under its responsibility, the parts of the facility that, because of the qualitative and quantitative characteristics of the material being implemented, stored, used or produced, are likely to be at the origin of a claim that may have direct or indirect consequences on the interests referred to in the facilityArticle L. 511-1 of the Environmental Code.
The operator shall provide fire and rescue services and inspection of classified facilities with a general plan of workshops and storages with a description of the hazards for each location with these risks and facilitating the operation of fire and rescue services.
Without prejudice to the provisions of Labour code, the operator has documents that allow it to know the nature and risks of hazardous products present in the facility, in particular safety data sheets.
The operator maintains a record of the nature and quantity of the inmate hazardous products to which a general storage plan is attached. This registry is available to fire and rescue services.
The premises are maintained clean and regularly cleaned, in particular to avoid clusters of hazardous or polluting materials and dust. Cleaning equipment is adapted to the risks posed by products and dust.
I. - Additional provisions for equipment that may release flammable dust:
A. - The installations are regularly disposed of, and at least once a year, of dust covering the ground, walls, supporting structures, cable paths, conduits, pipes, appliances and equipment.
The frequency of cleaning is determined under the operator's responsibility and specified in the organisational instructions. The cleaning dates are indicated on a register held at the disposal of the inspection of classified facilities.
Cleaning is, wherever possible, made using vacuum cleaners or suction plants. The appliance used for cleaning has all the safety features necessary to avoid fire and explosion and is suitable for products and dust. The use of other cleaning devices such as brooming or exceptionally compressed air is subject to special instructions.
Facilities are disposed of of any flammable product or material that is not necessary for the operation of the facility.
B. - Without prejudice to the provisions of Labour code, all provisions are implemented to limit the emission of dust in equipment (capotage, aspiration, gravity recovery system...).
C. - Arrangements are made to avoid an explosion or fire and to limit their spread and consequences when they occur. Access points (trappe or any other openings) are provided to allow rescue agents to project extinguishers within confined storages (recipients, silos, closed buildings).
D. - An automatic warning device signals any failure of the capture facilities that is not directly detectable by the occupants of the premises.
E. - The operation of production machines is ensured to the operation of aspiration equipment when they exist.
F. - The filters are under caissons and are protected by vents (except technical impossibility) leading to the outside.
The storage of recovered dust is carried out outside the workshop, outside of any hazardous area identified in section 8.
All measures are taken to avoid the formation of sparks.
I. - The closed structure has the following minimum fire reaction and resistance characteristics:
Work:
- external wall holders or pole-beam systems: R 60;
- internal separative walls: EI 60;
- floors/soil: REI 60;
- doors and closures: EI 60;
- roofs and roof coverings: BROOF (t3);
Township: DH 60;
Natural lighting: class d0.
Other premises and buildings have the following minimum fire reaction and resistance characteristics:
Work:
- exterior walls: R 30;
- Separative walls: EI 30;
- floors/soil: REI 30;
- doors and closures: EI 30;
Roofings and roof coverings: BROOF (t3);
Natural lighting: class d0.
The openings in the separative elements (passing ducts and pipes, conveyors) are equipped with fire-cutting devices equivalent to that required for these separative elements.
The surface of the mezzanines occupies not more than 50% of the surface of the floor level of the workshop.
The evidence of fire resistance properties is retained and maintained at the disposal of the inspection of classified facilities.
II. - The tunnels and tunnels of carriers/aspiration are designed to facilitate any maintenance, repair or cleaning of the carrier elements.
Storages are designed to reduce the number of areas that promote dust build-ups such as horizontal flat surfaces (excluding soils), wall coverings or soils that can not easily be dusted, piping entanglements, remote areas that are difficult to reach, weathered, etc.
I. - The operator shall provide fire and rescue services with specific instructions for accessing relief to all locations.
The facility has at least access at all times to allow fire and rescue services to be operated.
For the purpose of this Order, "access to installation" means an opening linking the service or public lane and the interior of the site sufficiently sized to allow the entry of emergency equipment and their implementation.
Vehicles whose presence is related to the operation of the facility station without causing any discomfort for the accessibility of emergency equipment from the external traffic lanes to the installation, even outside the operating and opening hours of the facility.
II. - Accessibility of equipment near the facility:
At least one "machine" track is kept clear for traffic on the perimeter of the installation and is positioned so that it cannot be obstructed by the collapse of any or part of the installation.
This "machine" track respects the following characteristics:
- the useful width is at least 6 metres, the free height at a minimum of 4.5 metres and the slope below 15%;
- in the inner radius bends below 50 meters, a minimum R radius of 13 meters is maintained and an overwidth of S = 15/R meters is added;
- the track is resistant to the carrying force calculated for a 320 kN vehicle with a maximum of 130 kN per axle, which is not more than 3.6 metres away;
- each point in the perimeter of the installation is at a maximum distance of 60 meters from this track;
- no obstacle is available between access to the installation or ladder lanes and the "machine" lane.
In the event of the impossibility of setting up a "machine" track allowing the traffic on the entire perimeter of the installation and if all or part of the track is stale, the last forty meters of the part of the stale track are of a minimum useful width of 7 meters and a 20-metre-diameter overturning area is expected at its end.
III. - Displacement of emergency equipment inside the site:
In order to allow the crossing of emergency equipment, any section of "machine" track of more than 100 linear meters has at least two so-called cross-roads, judiciously positioned, whose characteristics are:
- minimum useful width of 3 meters in addition to the equipment lane;
- minimum length of 15 meters,
presenting the same qualities of slope, bearing force and free height as the "machinery" path.
IV. - Ladder stationing:
For any equipment located in a building of height greater than 8 metres, at least two facades are served by at least one "scale" track allowing the circulation and stationing of the air scales. This ladder is directly accessible from the vehicle defined in II.
From this path, a ladder accessing at least the entire height of the building can be arranged. The track also respects the following characteristics:
- the useful width is at least 4 meters, the length of the parking area at least 10 meters, the slope at a maximum of 10%;
- in the inner radius bends below 50 meters, a minimum R radius of 13 meters is maintained and an overwidth of S = 15/R meters is added;
- no air obstacle hinders the manoeuvre of these scales vertically across the entire track;
- the distance from the facade is 1 meter minimum and 8 meters maximum for a parking parallel to the building and less than 1 meter for a parking perpendicular to the building;
- the track is resistant to the carrying force calculated for a 320 kN vehicle with a maximum of 130 kN per axle that is not more than 3.6 metres away and has a minimum punching resistance of 88 N/cm2.
In addition, for any equipment located in a multi-level building with at least one floor located at a height greater than 8 metres from the level of emergency access, on at least two facades, this "scale" path allows access to openings.
These openings allow at least one access per floor for each of the facades with ladder and have a minimum height of 1.8 metres and a minimum width of 0.9 metres. Obturation panels or frames that make these access open and remain accessible from outside and inside. They are easily identified from outside by emergency services.
V. - Establishment of the hydraulic system from the equipment:
From each "machine" or "scale" track is provided access to all exits of the building or at least two opposite sides of the installation by a stabilized path of at least 1.80 metres wide.
Fire-risk premises are partially equipped with natural smoke and heat evacuation devices (DENFC), in accordance with NF EN 12101-2, December 2003, allowing the free air evacuation of smoke, combustion gas, heat and unburned products in the event of a fire.
These devices are composed of automatic and manual (or self-control) control outlets. The useful opening surface of all outlets is not less than 2% of the surface to the local ground.
Natural smoke and heat evacuation devices are to be adapted to the specific risks of the installation.
In order to balance the swelling system and optimally distribute it, a useful area DENFC between 1 and 6 square meters is planned for 250 square meters of projected roof area.
In normal operation, rearming (closed) is possible from the floor of the premises or from the defensive zone. These manual opening controls are located near the access and installed in accordance with the NF S 61-932 or equivalent and up-to-date version.
The action of a security command cannot be reversed by another command.
All devices installed with reference to NF EN 12 101-2, version December 2003, have the following characteristics:
- Type B opening system (opening + closing);
- reliability: RE 300 class (300 safety cycles). Two-function outlets are subjected to 10,000 opening cycles in aeration position;
- the classification of the snow overload at the opening is SL 250 (25 daN/m2) for altitudes less than or equal to 400 metres and SL 500 (50 daN/m2) for altitudes greater than 400 metres and less than or equal to 800 metres. The SL0 class is usable if the location area is not likely to be snowed or if constructive provisions prevent snow accumulation. Above 800 metres, the outlets are SL 500 and installed with constructive provisions preventing snow accumulation;
- ambient temperature class T (00);
- heat exposure class B300.
Fresh air pipes of an area equal to the surface of the outlets are made either by openings on the façade or by mouths connected to ducts or by doors overlooking the outside.
I. - The facility is equipped with appropriate fire-fighting capabilities, including:
1° A means to alert fire and rescue services;
2° One or more fixed fire-fighting appliances (for example, water, poles) of a public or private network with a nominal diameter DN100 or DN150 implanted so that any point of the facility's limit is less than 100 metres from a device to provide a minimum flow of 60 cubic metres per hour for a period of not less than two hours and with a connection socket The aircraft are remote from a maximum of 150 metres (the distances are measured by the tracks practicable to fire and rescue equipment). If not, a water reserve of at least 120 cubic metres for extinction or any other equivalent means is accessible in all circumstances and at a distance from the facility having collected the advice of departmental fire and rescue services. This device has connections that comply with the standards in place to allow the fire and rescue service to feed and provide a flow of 60m3/h. The operator is able to justify to the prefect the effective availability of water flows and the dimensioning;
3° Distributed extinguishers within the installation when it is covered, on the outside areas and in places with specific risks, close to the clearances, well visible and easily accessible. Extinguishing agents are appropriate to the risks to be combated and compatible with stored materials.
II. - Fire control means are capable of operating effectively regardless of the temperature of the installation and especially during gel periods.
The operator shall ensure or perform the periodic verification and maintenance of the safety and fire control equipment in accordance with the applicable repositories. These audits are recorded on a register on which follow-ups to these audits are also mentioned.
The locations of fixed fire-fighting appliances and fire extinguishers are materialized on soils or buildings (e.g. by pictograms).
Pipes carrying dangerous or unhealthy fluids and collecting polluted or susceptible effluent are waterproof and are resistant to the physical and chemical action of the products they are likely to contain. They are properly maintained and are subject to appropriate periodic reviews to ensure their good condition.
In the parts of the installation referred to in Article 8 and identified as capable of causing an explosion, the electrical, mechanical, hydraulic and pneumatic systems conform to the provisions of the Decree of 19 November 1996.
The operator shall maintain at the disposal of the inspection of classified facilities the evidence that its electrical installations are carried out in accordance with the applicable rules, maintained in good condition and verified. These audits are recorded on a register on which follow-ups to these audits are also mentioned.
Metal equipment shall be grounded in accordance with applicable regulations and standards.
Materials used for natural lighting do not produce ignited drops during a fire.
If there is a boiler room, it is located in a room exclusively reserved for this effect or isolated from the rest of the installation by a REI 120 wall. Any possible communication between the boiler room and the other premises is done either by a sas equipped with two half-hour flame-shield doors, equipped with a door-farm or by a fire-fighting door EI 120.
Outside the boiler room are installed:
- a valve on the feed pipe of the burners, allowing to stop the flow of the fuel;
- a circuit breaker stopping the operation of the fuel pump;
- a sound and visual warning device, in the event of the malfunction of the burners, or another equivalent efficiency alert system.
The heating of the installation and its annexes can only be achieved by hot water, steam produced by a thermal generator or other system with an equivalent degree of safety.
The operator shall implement the provisions of section III of the aforementioned Order of October 4, 2010.
Without prejudice to the provisions of Labour code, the premises are properly ventilated to prevent the formation of explosive or toxic atmosphere. The outlet to the atmosphere of the ventilation is placed as far as possible from the buildings inhabited or occupied by third parties and the mouths of external air aspiration, and at a sufficient height given the height of the surrounding buildings in order to promote the dispersion of the gases rejected and at least 1 meter above the ridge.
The form of the evacuation pipe, particularly in the closest part of the outlet to the atmosphere, is designed to maximize the ascent and dispersion of the pollutants in the atmosphere.
Each technical room, technical cabinet or part of the facility identified according to the provisions of section 8 because of the consequences of a disaster that may occur has a smoke detection device. The operator lists these detectors with their functionality and determines maintenance operations to maintain their efficiency over time.
The operator is able to demonstrate the relevance of the selected dimensioning for these detection devices and, where applicable, automatic termination. It organizes, on a semi-annual basis, at least maintenance and testing checks in accordance with the existing repositories, which are kept at the disposal of the inspection of classified facilities. These audits are recorded on a register on which follow-ups to these audits are also mentioned.
In the event of installation of automatic fire-extinguishing systems, fire-extinguishing systems are designed, installed and maintained regularly in accordance with recognized repositories. These audits are recorded on a register on which follow-ups to these audits are also mentioned.
In the parts of the facility identified in accordance with the provisions of Article 8 due to the risk of explosion, the operator shall put in place blowlable vents/surfaces dimensioned according to the standards in force.
These blowlable vents/surfaces are arranged in such a way as not to produce man-made projection in case of explosion.
I. - Any storage of a liquid capable of creating pollution of water or soil is associated with a retention capacity of at least equal to the largest of the following two values:
100% of the capacity of the largest tank;
50% of the total capacity of the associated tanks.
This provision is not applicable to wastewater treatment basins.
For storage of unit capacity receptacles less than or equal to 250 litres, the retention capacity is at least equal to:
- in the case of flammable liquids, 50% of the total capacity of the drums;
- in other cases, 20% of the total capacity of the drums;
- in all cases 800 litres minimum or equal to the total capacity when it is less than 800 litres.
II. - The retention capacity is waterproof to the products it could contain and resist the physical and chemical action of the fluids. The same applies to its shut-off device which is kept closed.
The leakage of the (or) associated tank(s) must be controlled at any time.
Products recovered in the event of an accident may only be released under conditions consistent with this order or are disposed of as waste.
Containers or containers containing incompatible products are not associated with the same retention.
Storage of flammable liquids, as well as other toxic or dangerous products for the environment, is permitted under the soil level only in masonate or assimilated pit tanks, and for flammable liquids under the conditions set out above.
III. - When holdings are in the open air, they are emptied as soon as possible from rainwater spilling.
IV. - The soil of areas and premises for the storage or handling of hazardous materials for humans or likely to create pollution of water or soil is watertight and equipped so that it can collect washwater and commonly used materials accidentally.
V. - All measures are taken to collect all water and drainage that may be polluted during a disaster, including water used during a fire, so that the water is recovered or treated to prevent pollution of soils, sewers, streams or natural environment. This containment can be achieved by devices inside or outside the building. Inner devices are prohibited when dangerous substances are stored.
In the event of a containment device outside the building, the piped materials are collected, gravelly or through autonomous lifting systems, and then converge to this specific capacity. In the event of the use of autonomous lifting systems, the operator is able to justify at any time a rigorous maintenance and maintenance of these devices. Regular tests are also conducted on these equipment.
In case of containment inside the building, the flow holes are in the default closed position. In the event of an external containment, the flow holes from these devices are equipped with an automatic shut-down device to ensure this containment when water likely to be polluted is carried. Any means are put in place to avoid the spread of the fire by these flows.
The volume required for this containment is determined as follows. The operator calculates the sum:
- the volume of extinction water needed to fight the fire, on the one hand;
- the volume of product released by this fire, on the other hand;
- the volume of water associated with the weather at 10 litres per square metre of drainage surface to the containment work when the containment is external.
The collected extinction water is disposed of to the appropriate waste processing streams or released to the natural environment after being treated by one or more appropriate treatment devices to treat pollutants in the presence. In the event of a release to the natural environment, the operator will need to justify the lack of pollution created by this release.
The operator shall designate one or more reference persons with knowledge of the conduct of the facility, the hazards and disadvantages that its operation induced, the products used or stored in the facility and the provisions to be implemented in the event of an incident.
People outside the facility do not have free access to facilities.
In the parts of the facility identified in section 8, repair or development work may be carried out only after the development of a document or file comprising the following:
- the definition of hazardous activity phases and corresponding specific preventive means;
- the adaptation of equipment, facilities and devices to the nature of the operations to be carried out and the definition of their maintenance conditions;
- the instructions to be given to the persons in charge of the work;
- the organization set up to ensure first aid in the event of an emergency;
- when the work is carried out by an external company, the conditions of recourse by the latter to subcontract and the organization established in such a case to ensure the maintenance of security.
This document or file is prepared, based on an analysis of the risks associated with the work, and covered by the operator or by a person appointed by the operator. When the work is carried out by an outside company, the document or record is signed by the operator and the outside company or the persons they have named.
Compliance with previous provisions can be ensured by the development of the prevention plan defined in articles R. 4512-6 et seq. of the Labour Code where this plan is required.
In parts of the facility with fire or explosion risks, it is prohibited to bring fire in any form, except for work that has been the subject of a specific document or record in accordance with the preceding provisions. This prohibition is displayed in apparent characters.
An audit of the successful completion of the work is carried out by the operator or its representative prior to the resumption of the activity. It is registered and is made available for inspection of classified facilities.
Without prejudice to the provisions of Labour code, instructions are established, kept up-to-date and posted in places frequented by staff.
These instructions include:
- the prohibition to bring fire in any form, including the prohibition of smoking in areas with fire or explosion risks;
- the prohibition of any open air burning;
- the obligation of the "prevention plan" for the parties involved in the facility;
- the storage conditions of the products;
- emergency shutdown and installation safety procedures (electricity, fluid networks)
- measures to be taken in case of leakage on a container or piping containing dangerous substances;
- the modalities for the implementation of segregation devices of the collection network, as provided for in Article 22;
- means of extinction to be used in the event of a fire;
- the alert procedure with the telephone numbers of the facility's response officer, fire and rescue services, etc.;
- the obligation to inform the inspection of facilities classified in the event of an accident.
All staff, including acting, are trained in the application of these instructions.
The operation of the facility is compatible with the quality and quantity objectives of the water IV of Article L. 212-1 of the Environmental Code.
The prescribed emission limit values are those set out in this Order or those revised downward and presented by the operator in its file in order to incorporate the objectives set out in the above paragraph and to allow compliance, in the non-mix area environment, with environmental quality standards and threshold values defined by the above-mentioned Order of 20 April 2005 completed by the above-mentioned Order of 25 January 2010.
For each pollutant, the rejected flow is less than 10% of the eligible flow by the medium.
The design and operation of the facilities allows to limit water flows and pollutant flows.
Sections 27 to 31 and 34 to 37 apply only when water is collected for industrial use (for example, wood rolling).
The sampling is not in an area where permanent quantitative distribution measures have been instituted under theArticle L. 211-2 of the Environmental Code.
If the water removal is carried out, including by derivation, in a watercourse, in its accompanying table or in a water plan or channel fed by this watercourse or tablecloth, it is of a maximum capacity less than 1000 m3/h.
Open circuit refrigeration is prohibited.
Water sampling facilities are equipped with a totalizing measuring device. This device is recorded daily if the debit is likely to exceed 100 m3/d, weekly if the debit is lower. These results are stored on a registry that is eventually computerized and stored in the installation folder.
In the event of connection, on a public network or on a sheet drilling, the work is equipped with a disconnection device.
Direct connections between effluent collection networks to be treated or destroyed and the receiving environment are prohibited, with the exception of accidental cases where the safety of individuals or facilities would be compromised.
Aqueous effluent discharged by facilities is not likely to degrade the facility's networks or to release toxic or flammable products in these networks, possibly by mixing with other effluents. These effluents do not contain substances that hinder the proper operation of the site's processing facilities.
The collectors carrying water polluted by flammable liquids, or likely to be, are equipped with effective protection against the danger of flame propagation.
The effluent collection network plan shows the sectors collected, the points of connection, looks, swallows, lifting stations, measuring stations, manual and automatic valves. It is retained in the installation file.
effluent discharge points in the natural environment are as small as possible.
Releases allow good effluent diffusion in the receiving environment and minimize the mixing area.
The effluent discharge devices are designed to minimize the disturbance to the receiving environment, at the edge of the discharge point, depending on the use of the water in the immediate vicinity and on the swallow of the receiving environment, and not to hinder navigation.
On each effluent discharge pipe is provided a sample sampling point and measurement points (debit, temperature, polluting concentration...).
These points are located in a section whose characteristics (e.g., upstream conduct, wall quality, flow regime, etc.) allow for representative measurements to be made so that the speed is not substantially slowed down by thresholds or obstacles at the swallow and the effluent is sufficiently homogeneous.
These points are designed so as to be easily accessible and to allow safe interventions. All arrangements are also made to facilitate the intervention of organizations outside the application for inspection of classified facilities.
Unclean rainwaters that do not have an alteration of their original quality are evacuated by a specific network or in the natural environment if the specific network is non-existent and after justification by the operator of the absence of pollution created by this release.
Rainwater that is likely to be polluted, including run-off on traffic lanes, parking, loading and unloading areas and other waterproof surfaces, is collected by a specific network and processed by an adequate treatment device(s) to process pollutants in the presence.
These treatment devices conform to NF P 16-442 (version 2007 or later) or any other equivalent European or international standard.
These equipment are drained (hydrocarbons and sludges) and cured when the volume of sludge reaches half of the useful volume of the sludge and in all cases at least once a year, unless the operator's justification for the deferral of this operation on the basis of regular visual controls recorded and held at the disposal of the inspection. In any case, the postponement of this operation will not exceed two years. Follow-up sheets for the cleaning of deciant-separators of hydrocarbons, the standard compliance certificate, and waste-processing slips destroyed or retired are required for inspection of classified facilities.
Direct or indirect discharges of effluent to groundwater are prohibited.
All aqueous effluents are channeled.
Dilution of effluent is prohibited.
The requirements of this article apply only to direct releases to the natural environment.
The operator justifies that the daily maximum flow rate does not exceed 1/10 of the interannual average flow rate of the watercourse.
The temperature of the discharged effluent is less than 30 °C and its pH is between 5.5 and 8.5 or 5.5 and 9.5 if there is alkaline neutralization.
The color modification of the receiver medium, measured in a representative point of the mixing area, does not exceed 100 mg Pt/l.
For receiving water, releases do not induce outside the mixing area:
- a temperature rise greater than 1.5 °C for salmon water, at 3 °C for cyprinticultural waters and 2 °C for conchylic waters;
- a temperature greater than 21.5 °C for salmon water, 28 °C for cyprincultural water and 25 °C for water intended for food water production;
- pH outside of the following ranges of values: 6-9 for salmon, cyprincultural and bathing waters; 6.5-8,5 for water intended for food production and 7-9 for conchylic waters;
- an increase of more than 30% of the suspended material and a variation of more than 10% of the salinity for conchylic waters.
Residual waters released in the natural environment respect the following concentration limit values, according to the authorized maximum daily flow.
For each of the pollutants released by the installation, the maximum daily flow is to be specified in the registration file.
| Total suspension materials | 35 mg/l |
| DCO (sur effluent non déanté) | 125 mg/l |
| DBO5 | 30 mg/l |
Connecting to a collective, urban or industrial wastewater treatment plant is permitted only if the collective sanitation infrastructure (network and sewage station) is capable of transporting and treating effluent and the sludge resulting from this treatment in good conditions. Discharge authorization and, where applicable, a spill agreement shall be established with the competent authorities in charge of the remediation network and the collection network.
Channeled rainwater discharges meet the following concentration limit values, subject to the compatibility of discharges with the pollution levels defined below with the quality and quantity objectives of the water covered by the IV of Article L. 212-1 of the Environmental Code :
| Total suspension materials | 35 mg/l |
| DCO (sur effluent non déanté) | 125 mg/l |
| Total hydrocarbons | 10 mg/l |
| DBO5 | 30 mg/l |
Waste, waste, effluent and by-products is prohibited.
Dusts, gaseous pollutants or odors are collected at the source and channeled, except in the case of a justified technical impossibility. Without prejudice to the rules relating to occupational health and safety, releases are in accordance with the provisions of this Order.
Storages of pulverulent, volatile or fragrant products, which can lead to diffuse emissions of pollutants in the atmosphere, are confined (recipients, silos, closed buildings...). Handling facilities, transvasion, transport of these products are, unless justified technical impossibility, equipped with capture and suction devices to reduce emissions in the atmosphere. If necessary, the suction devices shall be connected to effluent treatment equipment to comply with the provisions of this Order. The associated equipment and fittings also meet the prevention of fire and explosion risks (events for drying towers, dust dusting towers...).
Treatment equipment is maintained at least once a year.
The operator shall be at the disposal of the inspection of the facilities classified the manufacturer data as well as the evidence that its processing equipment is carried out in accordance with the applicable regulations, maintained in good condition and verified at least annually. This check also contains the aspiration speed measurement.
In the event of a change in speed, the operator warrants whether or not it is appropriate to carry out more complete measures allowing a return to the nominal suction speed.
When the storage of pulverulent products is done in the open air, the humidification of storage or the spraying of additives to limit the flight in dry weather is permitted.
The storage of other bulk products (correls, green wood crushes...) is made to the extent possible in covered areas. In the absence of this, special provisions at both the design and construction level (wind-based installation) and the operation are implemented.
Release points in the natural environment are as small as possible. If several discharge points are required, the operator justifies this in its record.
The effluents are collected and released to the atmosphere, after possible treatment, through chimneys to allow proper release. The shape of ducts, particularly in their closest part of the outlet to the atmosphere, is designed to maximize the rise of gas in the atmosphere. The location of these ducts is such that there can be at no time siphoning effluent discharged in the pipelines or air catches nearby. The contours of the ducts are not angular and the variation of the section of the ducts in the vicinity of the outlet is continuous and slow.
The methods of measurement, sampling and analysis, of reference in force, are determined by the above-mentioned decision of 7 July 2009.
The height of the chimney (difference between the elevation of the open air outlet and the mean altitude of the ground at the place in question) expressed in meters is determined, on the one hand, according to the level of the emissions of pollutants to the atmosphere, on the other hand, depending on the existence of obstacles that may hinder the dispersion of the gases.
This height, which cannot be less than 10 metres, is the subject of justification in the file accompanying the application for registration, in accordance with the provisions of Appendix I.
The flow of gaseous effluent is expressed in cubic metres per hour in relation to normal temperature conditions (273 Kelvins) and pressure (101.3 kilopascals) after deduction of water vapour (dry gas). Pollutant concentrations are expressed in grams or milligrams per cubic metre relative to temperature and pressure conditions.
I. - Gas effluents respect the limit values in the table below according to the hourly flow. In the event that the same pollutant is emitted by various channelled releases, the limit values applicable to each channelled release are determined, where applicable, based on the total flow of all channelled and diffuse releases.
| 1. Total dust: | |
| Hourly flow less than or equal to 1 kg/h Hourly flow is greater than 1 kg/h | 40 mg/m3 100 mg/m3 |
The total dust releases of the installation do not exceed 50 kg/h.
II. - Limit values are required for medium measurements, samplings and analyses carried out over a half hour representative of the normal activity of the installation.
In the case of instantaneous sampling, no measurement results exceed double the prescribed limit value.
A total dust measurement is carried out at least every three years by an approved body.
In the case of these periodic measurements, the average of all measurements carried out during a monitoring operation does not exceed the emission limit values and none of the time averages is more than 1.5 times the emission limit value.
If the total hourly dust flow is greater than 5 kg/h, the operator conducts a daily assessment of its dust release. In the event that diffuse emissions represent a significant share of authorized flows, these emissions are periodically evaluated.
III. - In addition, for all other substances that may be released by the facility, the gaseous effluents meet the concentration limit values set out in the table according to the hourly flux set out in Appendix II.
IV. - The operator strives to reduce its biogenic VOC emissions, using available techniques at a reasonable cost.
All necessary steps are taken to ensure that the establishment is not responsible for the issuance of odorous gases that may inconvenient the neighbourhood and impair public health and safety.
Direct releases to soils are prohibited.
I. - Noise limit values:
The sound emissions of the facility are not at the origin, in the regulated-emerged areas, of an emergence greater than the eligible values defined in the following table:
| Higher than 35 and less than or equal to 45 dB (A) | 6 dB (A) | 4 dB (A) |
| Higher to 45 dB (A) | 5 dB (A) | 3 dB (A) |
In addition, the limit of ownership of the facility does not exceed, when in operation, 70 dB (A) for the day period and 60 dB (A) for the night period, unless the residual noise for the period under review is greater than that limit.
In the case where the particular noise of the establishment is marked tone within the meaning of point 1.9 of the schedule to the order of 23 January 1997 referred to, in an established or cyclical manner, its duration of appearance does not exceed 30% of the duration of operation of the establishment in each of the diurnal or nocturnal periods defined in the table above.
II. - Vehicles, construction equipment:
Transport vehicles, handling equipment and construction equipment used inside the facility are in accordance with the provisions in force for limiting their sound emissions.
The use of all acoustic communication devices (sirnas, tellers, loudspeakers, etc.), disturbing for the neighbourhood, is prohibited, unless their use is exceptional and reserved for the prevention and reporting of serious incidents or accidents.
III. - Operator monitoring of sound emissions:
The operator puts in place a monitoring of the sound emissions of the facility to estimate the value of the emergence generated in the regulated emerging areas. The measurements shall be carried out according to the method set out in the annex to the above-mentioned decision of 23 January 1997. These measurements are carried out under representative conditions of the operation of the facility for at least half an hour.
A measure of noise level and emergence must be carried out at least every three years by a qualified person or organization.
The operator shall make all necessary arrangements in the design and operation of its facilities to ensure the proper management of the waste of its business, including:
- limit the quantity and toxicity of waste to the source by adopting clean technologies;
- sort, recycle, value its by-products of manufacture;
- ensure, for ultimate waste whose volume must be strictly limited, storage under the best possible conditions.
The operator shall segregate waste (dangerous or non-dangerous) within the facility to facilitate their processing or disposal in specific industries.
The waste and residues produced are stored, prior to their revalorization or disposal, under conditions that do not pose a risk of pollution (prevention of meteorological water leaching, surface and groundwater pollution, flight and odours) for neighbouring populations and the environment.
Temporary storage, before recycling or disposal of hazardous wastes, is carried out on watertight and protected storage cuvettes of meteoric water.
The quantity of waste stored on the site does not exceed the monthly capacity produced or, in case of external processing, a normal batch of shipment to the disposal facility.
Wastes that cannot be valued are disposed of in regulated facilities environmental code. The operator is able to justify the removal on request of the inspection of classified facilities.
The operator sets up a register characterizing and quantifying all waste generated by its activities (nature, tonnage, disposal, etc.). It issues a tracking slip as soon as it delivers these hazardous waste to a third party.
Any open air burn is prohibited.
The operator shall establish a program to monitor its emissions under the conditions set out in section 45. The measures are carried out under the responsibility of the operator and at its own expense.
Inspection of classified facilities may, at any time, carry out or conduct samples of liquid or gaseous effluent, waste or soil, and perform or carry out measurements of sound levels.
The costs of sampling and analysis are borne by the operator.
The results of these measures are made available for inspection of classified facilities.
In the event that the operation of the facility would result in the direct or indirect emission of pollutants listed in the annexes to the above-mentioned 17 July 2009 Order, monitoring is in place to ensure that the introduction of these pollutants into groundwater does not result in significant and sustainable degradation or trends in the concentrations of pollutants in groundwater.
The operator declares its pollutant emissions and wastes in accordance with the thresholds and criteria of the amended January 31, 2008 Order relating to the register and annual reporting of pollutant emissions and wastes.
The Director General of Risk Prevention is responsible for the execution of this Order, which will be published in the Official Journal of the French Republic.
ANNEXES
Annex I
CALCUL RULES OF CHEMINATION
The amount s = k q/cm is calculated for each of the main pollutants where:
- k is a coefficient of 340 for gaseous pollutants and 680 for dust;
- q is the maximum instantaneous flow rate of the pollutant emitted to the chimney expressed in kilograms per hour;
- cm is the maximum concentration of the pollutant considered eligible for soil level as a result of the facility expressed in milligrams per normal cubic metre;
- cm is equal to cr - co where cr is a reference value given by the table below and where co is the annual average of the measured concentration at the place considered.
| Sulphur oxides | 0.15 |
| Nitrogen oxides | 0.14 |
| Pulses | 0.15 |
| Hydrochloric acid | 0.05 |
| Plomb | 0.000 5 |
| Cadmium | 0.000 5 |
In the absence of pollution measures, co may be taken on a flat basis as follows:
| Low-polluted area | 0.01 | 0.01 | 0.01 |
| Medium-planned or moderately industrialized area | 0.04 | 0.05 | 0.04 |
| Very urbanized or highly industrialized | 0.07 | 0.10 | 0.08 |
For other pollutants, in the absence of a measure, co may be neglected.
It is then determined that is equal to the largest of the s values calculated for each of the main pollutants.
The height of the chimney, expressed in metres, shall be at least equal to the hp value calculated as follows:
hp = s1/2 (R T)- 1/6
where:
s is defined above;
R is the gas flow expressed in cubic metres per hour and counted at the actual gas ejection temperature;
T is the difference expressed in kelvin between the temperature at the outlet of the chimney and the average annual temperature of the ambient air. If T is less than 50 kelvins, we adopt the value of 50 for the calculation.
If a facility is equipped with several chimneys or if there are other releases from the same pollutants to the atmosphere, the calculation of the height of the chimney is as follows:
Two chimneys i and j, respectively hi and hj, are considered dependent if the following three conditions are simultaneously met:
The distance between the axes of the two chimneys is less than the sum: (hi + hj + 10) (in metres);
hi is greater than half hj;
hj is greater than half hi.
This means that all the chimney-dependent chimneys of which the height is at least equal to the hp value calculated for the total mass flow of pollutants and the total volumic flow of the gases emitted by all these chimneys.
If there are natural or artificial barriers in the vicinity to disrupt the dispersion of gases, the height of the chimney must be corrected as follows:
- the hp value is calculated taking into account other releases when there are;
- structures and buildings are considered to be obstructions, including those housing the facility under study, which simultaneously meet the following conditions:
- they are located at a horizontal distance (expressed in meters) less than 10 hp + 50 of the axis of the chimney considered;
- they have a width greater than 2 meters;
- they are seen from the chimney considered from an angle greater than 15° in the horizontal plane;
- or hi the altitude (expressed in metres and taken relative to the average level of the ground at the place of the chimney) of a point of an obstacle located at a horizontal distance di (expressed in metres) of the axis of the chimney considered, and Hi defined as follows:
- if di is less than or equal to 2 hp + 10, Hi = hi + 5;
- if di is between 2 hp + 10 hp + 50, Hi = 5/4 (hi + 5) (1 - di/[10 hp + 50]);
- the largest Hp of the Hi values calculated for all points of all the obstacles defined above,
the height of the chimney shall be greater than or equal to the greater of the Hp and hp values.
The maximum continuous gas ejection speed is at least 8 m/s if the emission flow of the treated chimney exceeds 5,000 m3/h, 5 m/s if the flow rate is less than or equal to 5,000 m3/h.
ANNEX II
ELV FOR ATMOSPHÈRE
I. - Gas effluents respect the limit values in the table below. In the event that the same pollutant is emitted by various channelled releases, the limit values applicable to each channelled release are determined, where applicable, based on the total flow of all channelled and diffuse releases. For flow determination, channelled emissions and diffuse emissions are taken into account.
| 1. Total dust: | |
| Hourly flow less than or equal to 1 kg/h Hourly flow is greater than 1 kg/h | 100 mg/m3 40 mg/m3 |
| 2. Sulphur oxides (expressed in sulphur dioxide): | |
| Hourly flux greater than 25 kg/h | 300 mg/m3 |
| 3 . Nitrogen oxides (expressed in nitrogen dioxide): | |
| Hourly flux greater than 25 kg/h | 500 mg/m3 |
| 4. Hydrogen chloride and other inorganic chlorine gaseous compounds (expressed in HCl): | |
| Hourly flow greater than 1 kg/h | 50 mg/m3 |
| 5. Fluor and inorganic fluorine compounds (gas, vesicles and particles), (expressed in HF): | |
| Hourly flow greater than 500 g/h | 5 mg/m3 for gaseous compounds 5 mg/m3 for all vesicles and particles |
| Manufacturing units for phosphoric acid, phosphorus and phosphate fertilizers | 10 mg/m3 for gaseous compounds 10 mg/m3 for all vesicles and particles |
| 6. Volatile organic compounds (1): | |
| (a) General case: | |
| Total release of volatile organic compounds excluding methane: - total time flow exceeding 2 kg/h | 110 mg/m3(expressed in total carbon of the overall concentration of all compounds) |
| (b) Use of an oxidation technique to eliminate VOCs: | |
| Total release of volatile organic compounds excluding methane | 20 mg/m3 (total carbon) or 50 mg/m3 (total carbon) if the treatment yield exceeds 98% |
| NOx (NO2 equivalent) | 100 mg/m3 |
| CH4 | 50 mg/m3 |
| CO | 100 mg/m3 |
| (c) Specific volatile organic compounds: | |
| Total hourly flux of organic compounds exceeds 0.1 kg/h | |
| Actaldehyde (acetic aldehyde) | 20 mg/m3 (global concentration of all compounds) |
| Acrylic acid | |
| Chloracetic acid | |
| Formic Aldehyde (formaldehyde) | |
| Acrolein (acrylic aldehyde-2-propenal) | |
| Methyl acrylate | |
| Malian anhydride | |
| Aniline | |
| Biphenyls | |
| Chloroacetaldehyde | |
| Chloroform (trichloromethane) | |
| Chloromethane (methyl chloride) | |
| Chlorotoluene (Benzyl chloride) | |
| Cresol | |
| 2.4-diisocyanate toluylene | |
| Alkyated lead derivatives | |
| Dichloromethane (methylene chloride) | |
| 1,2-dichlorobenzene (O-dichlorobenzene) | |
| 1.1-dichloroethylene | |
| 2.4-dichlorophenol | |
| Diethylamine | |
| Dimethylamine | |
| 1.4-dioxane | |
| Ethylamine | |
| 2-furaldehyde (fural) | |
| Methacrylates Mercaptans (thiols) | |
| Nitrobenzene Nitrocrésol | |
| Nitrophenol | |
| Nitrotoluene | |
| Phenol | |
| Pyridine | |
| 1.1.2-tetrachloroethane | |
| Tetrachloroethylene (perchloroethylene) | |
| Tetrachloromethane (carbon tetrachloride) Thioethers Thiols | |
| O.toluidine | |
| 1.1.2-trichloroethane | |
| Trichloroethylene | |
| 2,4,5-trichlorophenol | |
| 2,4,6-trichlorophenol | |
| Triethylamine | |
| Xylènol (except 2,4-xylenol) | |
| (d) Substances to which hazard statements H340, H350, H350i, H360D or H360F or risk phrases R 45, R 46, R 49, R 60, R 61 and halogenated substances of H341 or H351, or labelled R 40 or R 68, as defined in the above-mentioned Order of 20 April 1994: | |
| Maximum time flow of the entire installation greater than or equal to 10 g/h | 2 mg/m3 in VOCs (value refers to the mass sum of the different compounds) |
| Halogenated organic compounds of hazard statements H341 or H351, or labelled R 40 or R 68: - maximum time flow of the entire installation greater than or equal to 100 g/h | 20 mg/m3 (value refers to the mass sum of the different compounds) |
| 7. Metals and compounds (gas and particulate matter): | |
| (a) Rejections of cadmium, mercury and thallium, and their compounds: | |
| Total hourly flux of cadmium, mercury and thallium, and their compounds exceeding 1g/h | 0.05 mg/m3 metal 0.1 mg/m3 for the sum of metals (expressed in Cd + Hg + Tl) |
| (b) Discharges of arsenic, selenium and tellure, and their compounds other than those referred to in 11: | |
| Total hourly flux of arsenic, selenium and tellure, and their compounds, exceeds 5 g/h | 1 mg/m3 (expressed in As + Se + Te) |
| (c) Releases of lead and compounds: | |
| Total lead and compound hourflow exceeds 10 g/h | 1 mg/m3 (expressed in Pb) |
| (d) Rejects of antimony, chrome, cobalt, copper, tin, manganese, nickel, vanadium and zinc, and their compounds other than those referred to in 11: | |
| Total antimony, chrome, cobalt, copper, tin, manganese (*), nickel, vanadium, zinc exceeds 25 g/h | 5 mg/m3 (expressed in Sb + Cr + Co + Cu + Sn + Mn + Ni + V + Zn) |
| 8. Releases of various gaseous substances: | |
| (a) Phosphine, phosgene: | |
| Hourly flux of phosphine or phosgene exceeds 10 g/h | 1 mg/m3 for each product |
| (b) Cyanhydric acid expressed in HCN, bromine and inorganic compounds of bromine expressed in HBr, chlorine expressed in HCl, sulphur hydrogen: | |
| Hourly flow of hydrocyanic acid or bromine and gaseous inorganic compounds of bromine or chlorine or sulphur hydrogen exceeds 50 g/h | 5 mg/m3 for each product |
| (c) Ammonia: | |
| Hourly ammonia flux exceeds 100 g/h | 50 mg/m3 |
| 9. Other fibres: | |
| amount of fibre, other than asbestos, implemented exceeds 100 kg/year. | 1 mg/m3 for fibre 50 mg/m3 for total dust |
| (1) The requirements of the c and d do not undermine respect for a and b. (*) And their compounds | |
II. - Limit values are required for medium measurements, samples and analyses carried out over a half-hour period.
In the case of instantaneous sampling, no measurement results exceed double the prescribed limit value.
In the case of a self-monitoring, as defined in section 59, permanent (at least one representative measure per day), none of the averages for twenty-four hours of normal operation exceeds the emission limit values and none of the mean hours is more than 1.5 times the emission limit value;
In the case of periodic measurements, the average of all measurements carried out during a monitoring operation does not exceed the emission limit values and none of the time averages is more than 1.5 times the emission limit value.
Guide to justification
As indicated in Article 3 of the above-mentioned Order, the operator shall enumerate and justify, as appropriate, all arrangements made for the design, construction and operation of the facilities to comply with the requirements of this Order. In particular, all justifications to be provided in the record file for the various articles of the order are described below. The same plan can include several information and descriptions.
Only the order is believed to fix the contents of the requirements to be justified.
| Article 1 | The installed electric power of the woodworking workshops is fixed by the operator in its registration file. | ||||
| Article 2 (definitions) | None. | ||||
| Article 3 (conformity of installation) | None. | ||||
| Article 4 (Scheduled installation) | None. | ||||
| Article 5 (location) | Localization plan and buildings. | ||||
| Articles 6 (flying dust) | Descriptions of planned measures. | ||||
| Article 7 (integration in landscape) | Descriptions of planned measures. | ||||
| Article 8 (Risk location) | General plan of workshops and storages indicating different risk areas. | ||||
| Article 9 (statement of stockpiles and hazardous products) | None. | ||||
| Article 10 (property of installation) | I: - equipment for cleaning areas; - plan of dust-emitting sources and their devices to limit dust emissions. | ||||
| Articles 11 (Fire performance) | Detailed layout of premises and buildings and description of constructive fire resistance provisions. | ||||
| Article 12 (accessibility) | Plan and descriptive note of planned accessibility provisions In the event of technical failure to comply with the provisions of section 12, the operator will propose equivalent measures to ensure access to the site for emergency services. These measures must have been agreed to by the Departmental Fire and Emergency Services (SDIS) and this SDIS certificate must be included in the record. These developments can then be instructed for advice from CODERST. | ||||
| Articles 13 (defense) | Description of the swelling device with note justifying the choices. | ||||
| Article 14 (fire fighting means) | Plan(s) and descriptive note of the safety devices in place, of the fire network independent of the industrial water network. Description of measures taken to ensure water availability in all circumstances. Where applicable, notice of departmental fire and rescue services with the details of the facility accepted for fire-aircraft (location, features and equipment). | ||||
| Article 15 (tuyauteries) | Plan of pipelines. | ||||
| Article 16 (material for use in explosive atmospheres) | Localization of affected areas. List of equipment envisaged. | ||||
| Article 17 (Electric installations and boilers) | Electrical installation plan and intended materials. Indication of the intended heating mode. Local heating and equipment planned. | ||||
| Article 18 (landing) | Lightning risk analysis and technical study. | ||||
| Article 19 (ventilation of premises) | Plan with location of outlets outside the ventilation of premises. | ||||
| Article 20 (detection system) | Description of the detection and extinction system. | ||||
| Article 21 (vents and blowlable surfaces) | Plan of vents and blowlable surfaces. | ||||
| Article 22 (retentions and site isolation) | List of areas and premises that may be affected and retention devices implemented with dimensioning calculation. Description of the measures taken to collect the waters likely to be polluted with a disaster. | ||||
| Article 23 (surveillance of installation) | Description of the access ban system. | ||||
| Article 24 (travaux) | None. | ||||
| Article 25 (Operation marks) | None. | ||||
| Article 26 (General principles on water) | When the discharge occurs in a watercourse, it specifies the name of the watercourse, the name of the water mass and the kilometric point of discharge. It indicates whether the release is carried out in a sensitive area as defined under theArticle R. 211-94 of the Environmental Code. The quality and quantity objectives are set in the SAGEs, SDAGEs and measurement programs at each watershed level. These data and documents are available from water agencies. For each of the parameters of section 26, the calculation from the following formula must be provided. 10 % x NQEparameter x Thickness flow rate of watercourse ‡ VLE x Maximum industrial discharge flow NQE for the different parameters are available in the January 25, 2010 order and in the May 7, 2007 circular. The stretching rate (QMNA5) is available on the website: http://www.hydro.eaufrance.fr or from water agencies (see Internet addresses above). The ELVs are set out in Article 36 of this Order. When the release occurs in an STEP, it specifies the name of the STEP. Subject to the provision of the discharge authorization in the record or failing the authorization, a letter from the STEP manager indicating the acceptance of the effluents, the facility is then considered to be in compliance with the requirements of this section. | ||||
| Article 27 (water pupil) | Installation plan and descriptive note of drilling and/or sampling. Justify that sampling is not in an area where permanent quantitative distribution measures have been instituted under theArticle L. 211-2 of the Environmental Code (Water distribution area, RTA). These areas are fixed by prefectural arrest and are available in prefecture. Otherwise, in the event of a sampling in RTA, the threshold of 80m3/h may be reduced to 8 m3/h upon request of the operator who will justify the compatibility of this sampling with the RTA rules and prescribed by APC. Indicate the maximum volume of daily sampling carried out in the public and/or natural environment and according to the type of sampling, justification for compliance with the thresholds taken in section 32. Description of refrigeration processes implemented where applicable. | ||||
| Article 28 (books of sampling) | Plan and descriptive note of sampling works. | ||||
| Article 29 (collection of effluents) | effluent collection networks plan. | ||||
| Article 30 (points of rejection) | Plan of rejection points. | ||||
| Article 31 (points of sampling for inspection) | Plan including the position of sampling points. | ||||
| Article 32 (rejections of rainwater) | An indication of the environment in which rainwater is rejected. Plan of networks and treatment devices and note justifying dimensioning. | ||||
| Article 33 (underground water) | None. | ||||
| Article 34 (VLE - generalities) | None. | ||||
| Article 35 (debit, temperature and pH) | Specify the maximum discharge rate, release temperature, if discharge occurs in the natural environment or STEP. Note justifying compliance with the rejection criterion if released to the natural environment. If the natural environment temperature criterion cannot be met, the operator must justify that the waters in which its discharges are made are not salmon (data available from the prefecture). | ||||
| Articles 36 (ELV - natural environment), 37 (returning to a depuration station) | Indication of the environment in which effluents are released. If applicable, the operator justifies that the installation of pre-treatment and/or internal treatment at the facility has an adequate puratory performance based on a contractual commitment from the treatment system provider. | ||||
| Article 38 (colours of rainwater) | None. | ||||
| Article 39 (cleaning) | None. | ||||
| Article 40 (General principles on air) | Plan and descriptive note of arrangements for storing products. If these provisions are not necessary, note the justification. | ||||
| Article 41 (points of rejection) | Plan and descriptive note of arrangements for capture and possible treatment of air emissions. Plan of rejection points, if applicable. | ||||
| Article 42 (points of action) | Plan of measurement points, if applicable. | ||||
| Article 43 (fridge height) | Plan and calculation note of chimney heights, if applicable. | ||||
| Articles 44 and 45 (ELV) | None. | ||||
| Article 46 (odors) | Description of provisions to limit odours, if necessary. | ||||
| Article 47 (emissions in the ground) | Rationale for the absence of direct releases to the soil. | ||||
| Article 48 (noise and vibration) | Description of provisions to limit noise. | ||||
| Articles 49, 50 and 51 (waste) | Note describing the type, nature, quantity and off-site treatment of waste produced, a table of this type is provided: | ||||
| Type of waste | Waste codes (Article R 541-8 of the Environmental Code) | Nature of waste | Total production (maximum annual tonnage) | Off-site treatment mode | |
| Non-hazardous waste | |||||
| Hazardous wastes | |||||
| Article 52 (VLE) | Monitoring program (dusts). | ||||
| Article 53 (impact on groundwater) | Please indicate whether pollutants are issued in the appendices to the 17 July 2009 Order. If emissions of pollutants appearing in the appendices to the 17 July 2009 Order present the monitoring set up. | ||||
| Article 54 (annual reporting of pollutant emissions) | None. | ||||
| Article 55 (execution) | None. | ||||
Done on September 2, 2014.
For the Minister and by delegation:
The Director General of Risk Prevention,
P. White
