Key Benefits:
Minister of Ecology and Sustainable Development,
Seen Council Directive 90/667 of 27 November 1990 amending Directive 90/425 laying down health rules on the disposal and processing of animal waste;
Having regard to Regulation (EC) No 1774/2002 of the European Parliament and of the Council of 3 October 2002 laying down the health rules applicable to animal by-products not intended for human consumption;
In the light of the Council Directive of 15 July 1975 on waste (75/442/EEC), as amended by the Council Directive 18 March 1991 (91/156/EEC);
Having regard to the Council Directive of 12 June 1986 on the protection of the environment, in particular the soil, in the use of sewage sludge in agriculture (86/278/EEC);
Given the environmental code ;
In view of Decree No. 77-1133 of 21 September 1977, as amended for the purposes of Act No. 76-663 of 19 July 1976 on classified installations and Title I of Act No. 64-1245 of 16 December 1964 on the system and distribution The waters and the control of their pollution;
In accordance with Decree No. 91-1283 of 19 December 1991 concerning quality objectives assigned to watercourses, stream sections, canals, lakes or ponds and the waters of the sea within territorial limits ;
Having regard to Decree No. 92-1042 of 24 September 1992 on the application of Article 5 of Law No. 92-3 of 3 January 1992 on water and on water management and management schemes;
Having regard to the Order of 30 December 1991 concerning the Animal waste processing and the production of animal feed;
In the opinion of the Board of Governors of the facilities classified as of June 27, 2002,
Stop:
This Order sets out the requirements for classified installations subject to authorisation under heading 2730 of the nomenclature.
It applies in particular to installations providing for the Treatment by washing, drying and handling of new feathers and duvets and/or recovery feathers and duvets.
The provisions of this Order shall apply to orders for the authorization of new and existing classified installations Provisions set out in Chapter VIII.
The prefectural authority for the authorization of an installation may, as appropriate, fix more stringent provisions than those prescribed in this Order.
For the purposes of this Order, installation means:
-the buildings in which the Operations for the reception or processing of raw materials, including the remains where appropriate;
-the annexes: storage sheds for the materials derived from the treatment (in particular, flours and skins), storage and treatment devices Effluents, truck wash stations used to transport corpses, wastes and by-products of animal origin, biofilter.
Treatment by dehydration means a thermal treatment under pressure to obtain Flours.
The installation must be installed:
-at least 200 metres from the homes occupied by third parties or Premises usually occupied by third parties, stadiums or registered campgrounds (with the exception of on-farm campgrounds) as well as areas for habitation by urban planning documents against third parties;
-to the Less than 35 metres of the wells and boreholes outside the site, sources, open-flow aqueducts, any underground or semi-buried installation used for the storage of drinking water, shorelines, Stream banks;
-at least 200 metres from public bathing sites and beaches;
-at least 500 metres from the river farms subject to authorisation or declaration under heading 2130 of the nomenclature and zones The
lot of dead bodies, waste and by-products of animal origin shall be installed at least 100 metres from the dwellings occupied by third parties.
The provisions of this Article shall apply in the case of extensions of existing installations only to new buildings. They do not apply when the existing installations are brought into compliance.
The site must be closed by a Resistant material on a minimum height of 2 metres prohibiting unauthorised entry inside the site. All operations within the facility must be subtracted from the public view; vegetation screens are set up where appropriate.
A sign and information panel of resistant materials is placed in the immediate vicinity of the main entrance. It shall be legibly and indelibly marked as follows:
(installation description)
Animal waste treatment plant of animal origin
subject to authorisation under Article L. 512-2
of the
Prefectural authorization (n °) of (date)
(social reason) and (operator's address)
PROHIBITED NOT AUTHORIZATION
The organization of vehicle traffic inside the site must allow for compliance with the health principle of the forward step.
The traffic plan inside the site Site must be displayed and monitoring means must be implemented to control inputs and outputs at all times.
The operator takes appropriate steps to integrate the operation into the landscape.
The entire installation is maintained and maintained on a permanent basis.
The approaches to the installation, placed under The control of the operator, are arranged and maintained in good condition of cleanliness (painting ...). Discharge emissaries and their periphery are the subject of special care (planting, engazing ....).
Soil Traffic and garage tracks other than those connected to the parking of vehicles after washing and disinfection shall be watertight and equipped in such a way as to be able to collect wash water, accidentally spread products and water Fire-extinguishing potential.
The operator has sufficient supplies of consumable products or materials Used routinely or occasionally to ensure the protection of the environment such as filters, neutralization products, inhibitory liquids, absorbent products
The operator shall make the necessary arrangements in Design, construction and operation of facilities to limit the risks of nuisance and accidental pollution of air, water or soil. Dehydration treatment devices for corpses, wastes and by-products of animal origin, as well as effluent treatment devices, must be properly maintained in order to avoid prolonged outages. During their accidental shutdown or for technical reasons, all measures must be taken to avoid the waiting in place of the raw materials at room temperature.
Reception areas and storage facilities for dead bodies, waste and by-products Shall be under closed building to limit odour damage in the vicinity of the facility, including the installation of automatic access doors.
These areas shall also be watertight and equipped with Such that the juices of corpses, waste and by-products of animal origin cannot directly reach the natural environment and are collected and processed in accordance with the provisions of Article 19
The storage of dead bodies, waste and by-products of animal origin must be Constructed of impermeable, shock-resistant materials that are easy to clean and disinfect.
The soil must be watertight, resistant to the passage of equipment and vehicles for unloading corpses, waste and By-products of animal origin and designed to facilitate the flow of drip juices and cleaning water to collection facilities.
The premises must be properly lit and allow for the protection of waste Weather and heat.
Storage before treatment shall not exceed 24 hours if corpses, waste and By-products of animal origin are stored at room temperature. For installations not dealing with dehydration, the storage period must not exceed 24 hours before departure.
These delays can be extended if all the dead bodies, waste and by-products of animal origin are Maintained at a temperature below + 7 ° C. In this case and for dehydration installations, the treatment shall start immediately after the exit of the enclosure maintained at that temperature.
The capacity of these premises shall be compatible with the processing time and Allow for unannounced stops.
In establishments dealing with dehydration, corpses, waste Or by-products of animal origin, the fragrant molecules of the storage buildings of dead bodies, waste and by-products of animal origin before on-site treatment at a temperature greater than + 7 ° C shall be collected and processed using Adapted and effective devices, for example by a depression followed by treatment.
All premises of Storage of raw materials shall be kept in a good state of cleanliness and shall be cleaned at least twice a week. The frequency of cleaning is daily for the working premises (draft, grinding, etc.).
The installation must have adequate equipment to clean and disinfect containers or containers in which the animal waste is Receptacles, as well as the vehicles in which they are transported.
Containers, containers and vehicles used for the transport of animal waste must be cleaned and washed after each use and disinfected regularly and in the Minimum once a week (indoor and outdoor).
The wheels of the transport vehicles must in particular be disinfected after each use.
Collection and transport of corpses, waste and animal by-products Must be carried out in watertight containers or containers with liquids and closed the time of transport.
All Storage of a liquid capable of creating pollution of water or soil and, in particular, the storage unit of the waters having been in contact with the corpses, waste and by-products of animal origin shall be associated with a holding capacity of which the 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.
This provision is not applicable to treatment tanks Waste water.
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 capacity Total of drums;
-in other cases, 20 % of total barrels capacity;
-in all cases, 800 litres minimum or equal to total capacity where this is less than 800 litres.
Retention capacity is watertight Products that it could contain and resist the physical and chemical action of fluids. The same is true for its sealing device which is kept closed.
The integrity of the associated tank (s) must be capable of being controlled at any time.
Products recovered in the event of an accident can only be released in Conditions in accordance with this Order.
Tanks or containers containing incompatible products are not associated with the same retention.
Storage of flammable liquids and other products, toxic, corrosive or Dangerous to the environment is permitted below ground level only in storage tanks, or assimilated and, for flammable liquids, under the conditions set out above.
The operator has the documentation to know the nature and risks of the hazardous products present in the installation; The security data provided for in the Labour Code makes it possible to meet this obligation.
Within the licensed installation, drums, tanks and other packaging shall bear in very legible characters the names of the products and Hazard symbols according to, if applicable, the regulations for the labelling of dangerous chemical substances and preparations
The effluents collected on the site belong to one of the 3 categories
-uncontaminated stormwater;
-soiled waters and waters that have been in contact with raw materials or surfaces soiled by raw materials;
-other waters (for example, wash water, Including wash water, bleed water, valve water ...).
Different effluents are treated in the manner
-the uncontaminated stormwater is released to the natural environment or the storm system serving the facility, if it exists;
-the waters having been in contact with raw materials or with susceptible areas To be soiled by raw materials must be treated in accordance with the provisions of Article 36;
-other waters shall be cleaned, where treatment is necessary to comply with the limit values imposed on the discharge and defined In Annex I.
The effluent treatment facility shall have a sealed, closed, Capacity to deal with the site's operational hazards
The installation must be equipped with a watertight containment basin. This basin must be able to collect all the waters that may be polluted in an accident or fire, including the water used for the purpose of extinguishing.
The volume of this basin is determined by the hazard study.
In Absence of supporting evidence, a lump sum value of at least 5 m³ per tonne of flour and stored fat is retained. The control organs necessary for the establishment of this pool must be able to be operated in all circumstances, locally and from a control station. The waters collected shall be treated in accordance with the provisions of Article 19
The operator shall take all necessary steps in the design and operation of the facilities to limit the flow of water. A level of water consumption per tonne of raw materials processed must be defined in particular.
In case of Connection on a public network, the book is equipped with a disconnection device. The volumes of water used from a public network are measured by the meter which is equipped with the connection of the facility.
Water sampling works shall not interfere with the free flow of water. Where they are to be constructed in the bed of the watercourse, they shall respect, without prejudice to any authorization required pursuant to Article L. 432-3 of the Environment Code, the provisions of Articles L. 432-5 and L. 432-6 Of the code. Their implementation is consistent with the water management and management plan provisions and the water management and management scheme, where it exists. Each sampling point in the soil or watercourse must be equipped with a totalizing time meter.
The volumes consumed must be recorded daily if the flow rate is likely to exceed 100 m³ /d and in a manner that Weekly if this flow rate is lower; they are recorded in a potentially computerized register kept available for inspection of classified installations.
When drilling oil wells, all steps are taken to avoid communication of separate water bodies, unless explicit permission is given in the order In order 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
The completion of a new drilling or the decommissioning of a borehole is brought to the attention of the prefect with all the elements of assessment of the hydrogeological impact
Processing conditions and emission limit values are set in The authorisation order on the basis of the use of the best available technologies at an acceptable economic cost and the particular characteristics of the environment.
Rejection points in the natural environment are as small as possible.
Release structures should allow for good diffusion of effluents into the environment Receptor.
Releases to the atmosphere are to the extent possible collected and evacuated, after treatment if necessary, through technical means for good release of releases.
In the case of chimneys, the form Ducts, especially in the area closest to the outlet to the atmosphere, are designed to maximize the rise of gases in the atmosphere. The terminal portion of the stack may have a converged convergence according to the rules of the art when the ejection rate is higher than the rate chosen for the gas in the stack. The location of these ducts is such that there can be no siphoning of effluent discharged to nearby ducts or intakes at any time. The contours of the ducts are not angular, and the variation of the ducts in the vicinity of the outlet is continuous and slow.
The collection piping of liquid or susceptible liquid effluents is watertight and resists the physical and chemical action of the products that they are likely to contain. They are properly maintained.
The various pipes are located in accordance with the rules in force.
A schematic of all the networks and a sewer plan are established by the operator, regularly updated and dated, In particular after every notable change. They shall be made available for inspection of classified installations, as well as fire and rescue services. The plan shall show the areas collected, the connection points, gazes, swallows, measurement stations, manual and automatic valves, etc.
With the exception of accidental cases where the safety of persons or installations would be It is prohibited to establish direct links between the receiving environment and the effluent collection systems to be treated or destroyed.
In installations treating by dehydration the corpses, waste or by-products of animal origin, the level of an odor or concentration of a fragrant mixture is defined as The dilution factor to be applied to an effluent so that it is no longer felt as fragrant by 50 % of the population in accordance with the standard NF X 43-101, X 43-104 then NF EN 13725, six months after Publication in the collection of AFNOR standards.
The odour rate is conventionally defined as the product of the rejected air flow, expressed in m³ /h, by the dilution factor at the perception threshold (or odour level) expressed as a number of units Odour per m³.
Odour flow is calculated on the basis of an atmospheric dispersion study that takes into account local conditions of dispersion of air pollutants. The odour rate shall meet the following ambient air quality objective: the odour concentration calculated within a radius of 3 kilometres in relation to the limits of the installation shall not exceed five odour units per m³ more than 175 Hours per year (a frequency of 2 %) for existing facilities or more than 44 hours per year (a frequency of 0.5 %) for new installations.
The overrun frequency must take into account possible durations Unavailability of odour-based treatment facilities.
This dispersion study shall be carried out by a competent body chosen in agreement with the inspector for classified installations, at the expense of the operator and under his
In the absence of a dispersion study, the odour concentration to be retained, regardless of the emission height, shall not exceed 1 000 ouE/m³ (European scent units per cubic metre)
The dispersion of odours in the ambient air of the receiving and storage facilities of the raw material must be limited to More possible:
-reducing storage time before processing;
-ensuring the permanent closure of the receiving, storage and draft buildings, if any, of animal-sourced corpses, wastes and by-products;
-avoiding odor clearances such as grinders and transfer screws through the placement of hoods or hoods;
-by proper cleaning and disinfection of the premises.
In installations treating by dehydration the corpses, waste or by-products of animal origin all cold fragrant gas from the Raw materials for receiving, draft, and milling facilities are collected and directed to a processing facility.
All cooking gases and gas from the workshops must be collected by hoods or captives at the emission points and in particular:
-pre-cook loading and unloading stations, Cookers, hydrolyzers, etc. ;
-the vacuum pump exhaure of the cookers and thighs;
-a buffer between two workstations;
-transfer screws;
-pressing installation, sieving;
-dryers.
The collected gaseous effluents are directed by circuits made in corrosion materials to pre-treatment and/or Treatment.
Releases to air should be cleaned up.
Stack height (difference between altitude The outlet to the open air and the average altitude of the ground at the point considered) expressed in metres is determined, on the one hand, according to the level of the emissions of pollutants to the atmosphere, on the other hand, according to the existence of potential obstacles To interfere with gas dispersion.
This height, which cannot be less than 10 metres, is fixed by the authorization order.
Releases to the atmosphere, as measured under regulatory conditions, expressed on dry gas after deduction of water vapour and reported at a concentration of 11 % of oxygen on dry gas will contain less than :
1 ° Total Poussières:
If the time flow is less than or equal to 1 kg/h, the concentration limit value is 100 mg/m³.
If the time flow is greater than 1 kg/h, the concentration limit value is 40 mg/m³.
2 ° Monoxide Carbon:
The prefectural authorization decree sets a limit value for carbon monoxide. It shall not exceed 100 mg/Nm³.
3 ° Sulphur oxides (expressed in sulphur dioxide): if the hourly flux is greater than 25 kg/h, the concentration limit value is 300 mg/m³.
4 ° Oxides of nitrogen (excluding nitrogen protoxide) Nitrogen dioxide):
If the hourly flux is greater than 25 kg/h, the concentration limit value is 500 mg/m³.
5 ° Hydrogen chloride and other inorganic gaseous compounds of chlorine (expressed in HCl): If the hourly flux is greater than 1 kg/h, the concentration limit value is 50 mg/m³.
6 ° Fluorine and inorganic fluorine compounds (gas, vesicles and particles) (expressed in HF): If the hourly flux is greater than 500 g/h, the concentration limit value is 5 mg/m³ for The gaseous compounds and 5 mg/m³ for all vesicles and particles.
7 ° Total organic carbon:
The limit value is 20 mg/Nm³ of total organic carbon.
8 ° Sulphidic Hydrogen:
If the hourly flow of hydrogen sulphide Exceeds 50 g/h, the concentration limit value is 5 mg/m³.
9 ° Ammonia:
If the hourly ammonia flux exceeds 100 g/h, the concentration limit value is 50 mg/m³.
10 ° Dioxins and furans:
The limit value of Concentration is 0.1 ng/m³. It shall be measured over a sampling period of at least six hours and a maximum of eight hours and refers to the total concentration of dioxins and furans calculated using the concept of toxic equivalency.
In the case where a facility rejects the same pollutant by various channelized releases, the provisions of section 34 Apply to each channelized rejection if the total flux of all the channelled and diffuse releases exceeds the threshold set out in Article 34.
The following provisions apply to waters that have been in contact with raw materials or surfaces that may be contaminated by raw materials:
I.-Facilities dealing with Corpses, waste or by-products of animal origin whose destruction is made compulsory must comply with one of the following obligations:
-be equipped with a device to ensure the absence of Liquid discharge;
-ensure liquid effluent is autoclaved at 133 ° C for 20 minutes under pressure of 3 bars without interruption and be equipped with a filtration device to hold particles larger than 10 µ m or any other device deemed equivalent, and comply with the discharge standards set out in Schedule I.
II. -Installations dealing with corpses, waste or by-products of animal origin whose destruction is not regulated by regulation shall comply with the emission standards laid down in Annex I.
For installations that do not Not by dehydration, the effluent can be treated on site or at an authorized plant.
I. -For installations referred to in paragraph I of Article 36, sludge and waste from the wastewater treatment plant shall be treated by a incineration or co-incineration plant, directly or after Dehydration.
II. -For installations referred to in paragraph II of Article 36, materials of animal origin collected during the pre-treatment of waste water, in particular refusal of relief and screening, shall be dealt with in accordance with the provisions Regulations in force including: incineration or co-incineration directly or after dehydration; landfill, composting, processing into fertilizers, amendments or biogas after autoclaving at 133 ° C for 20 minutes under one Pressure of 3 bars without interruption, or any other recognized hygienic method of equivalent effectiveness. Sludge from water treatment plants may be applied in accordance with the provisions laid down in Annex II.
Flours of animal origin must be stored in enclosed and enclosed enclosures. The soil must be flat and waterproof. The roof, carrier structure and soil are non-combustible. The walls and roof must be kept watertight in such a way that the stock of flour is not humidified. The building must be equipped with an extinguishing device.
All arrangements are made to prevent contact with the flours with the water, including rainwater and runoff.
Inside the enclosure, air circulations Must not cause the flight of particles of flour. The top of the stock is arched in order to avoid the thermal draw observed in conical storage. The height of the pile of flour does not exceed 7 metres. The form and slope of the pile must limit the risk of creep of the meal. Storage is designed to allow storage and management of the stock.
The moisture content of the meal should be kept as low as possible (< 15 %). Flours with significantly different moisture levels should be stored separately, to avoid the risk of heating.
An area is reserved for the possible cooling of the meal. The surface of the cooling area must be at least 10 % of the total area of the storage.
Flour loading operations are carried out in a confined space to limit the flight of particles. The washing waters of the areas where the meal is stored shall be treated in accordance with the provisions of Article 36.
Waste and by-products are stored, prior to their recovery or disposal, under conditions that do not pose a risk of pollution (prevention of leachate by meteor waters, surface water pollution, and For the surrounding populations and the environment.
Temporary storage, prior to recycling or disposal of special waste, is carried out on watertight and protected water holding tanks
The transport of animal waste and animal by-products not intended for human consumption must comply with the health regulations in force.
Before departure, vehicles that have been circulated on a soiled area Must be cleaned properly.
Wastes that cannot be recovered are disposed of in Installations regulated for this purpose under Book V of the Environment Code, under conditions for the protection of the environment; the operator shall be able to justify the disposal on request of the inspection of the Classified facilities. It will make available to the inspection of facilities classified as a characterization and quantification of any special waste generated by its activities.
Any burning of waste in open air is prohibited.
Food of Animal Origin from Large and Medium Surfaces, Agri-Food Industries and Distribution channels can only be collected and introduced into the installation if they have been previously released from packaging and packaging.
The authorization decree sets out the conditions for the disposal of the various waste generated by the installation and in particular the characteristics and maximum quantities of waste Solid that the operator is authorized to store.
The sound emissions from the facility comply with the provisions of The decree of 23 January 1997 on the limitation of noise emitted to the environment by classified installations.
The installation shall be 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 for The
emitted comply with the technical rules annexed to the circular of 23 July 1986 concerning mechanical vibrations emitted to the environment by the classified installations.
I. -Where permitted pollutant flows exceed thresholds with concentration limits, the operator shall establish a monitoring program for its emissions. The measures shall be carried out by the operator or under its responsibility and at its own expense under the conditions laid down by the authorisation order.
The authorisation decree establishes the nature and frequency of the measures defining the monitoring programme Emissions. Depending on the characteristics of the facility or the sensitivity of the environment, other pollutants other than those mentioned in this order may be affected or lower thresholds may be defined.
II. -For the implementation of the monitoring program, the methods used are standard reference methods. The authorisation decree may provide for other methods where the results obtained are equivalent to those provided by the reference methods. Similarly, it may provide for the replacement of certain monitoring measures with the monitoring of a representative parameter of the pollutant or by any other equivalent method. Where methods other than the reference methods are used, control and calibration measures shall be carried out periodically, at a frequency fixed in accordance with the inspection of classified installations, by an external body
III. -The results of all measures shall be sent to the inspection of classified installations on a monthly basis, accompanied by written comments on the causes of any overruns, as well as on corrective actions taken Work or contemplated.
IV. -The inspection of classified installations may at any time carry out sampling of liquid or gaseous effluents, waste or soil, and carry out measurements of sound levels. The cost of sampling and analysis shall be borne by the operator.
Where releases to the atmosphere of pollutants The operator shall carry out, under the conditions laid down in Article 45, an ongoing measure of the flow of the corresponding discharge and the measures set out below. In the case where non-point emissions represent a significant portion of the permitted flows, these emissions are evaluated periodically.
1 ° Total Flows:
If the hourly flux exceeds 50 kg/h, the continuous measurement of dust emissions By a gravimetric method is carried out.
Where the dust contains at least one of the metals or metal compounds listed in Article 27 of the decree of 2 February 1998, and if the hourly flux of the canalised emissions of dust exceeds 50 G/h, the continuous measurement of dust emissions is carried out.
If the hourly flow exceeds 5 kg/h, but is less than or equal to 50 kg/h, an ongoing assessment of the dust content of the releases using, for example, an opacimeter Is performed.
2 ° Carbon monoxide:
If the hourly flow exceeds 50 kg/h, the constant measurement of carbon monoxide emissions is achieved.
3 ° Sulphur oxides:
If the hourly flow exceeds 150 kg/h, the measurement is ongoing Sulphur oxide emissions are achieved.
4 ° Oxides of nitrogen:
If the hourly flux exceeds 150 kg/h, the continuous measurement of nitrogen oxide emissions is achieved.
5 ° Hydrogen chloride and other inorganic gaseous compounds of the Chlorine:
If the hourly flux exceeds 20 kg/h, the continuous measurement of hydrogen chloride emissions is performed.
6 ° Fluorine and fluorine compounds:
If the hourly flux exceeds 5 kg/h, the continuous measurement of gaseous emissions from Fluorine and fluorine compounds is carried out, as well as the constant measurement of total dust. A daily measurement of the fluorine contained in the dust is made on a representative sample taken continuously.
7 ° Volatile organic compounds: Volatile organic compound " (VOC), any organic compound, excluding methane, having a vapour pressure of 0.01 kPa or more at a temperature of 293.15 ° K or having a corresponding volatility under specific conditions of use.
Monitoring in Continuous emissions of all VOCs to the exclusion of methane is achieved if, throughout the installation, one of the following conditions is met:
-the maximum hourly flux of VOCs to the exclusion of total carbon methane Exceeds:
-15 kg/h in the general case;
-10 kg/h if a VOC-laden gas cleaning equipment is required to meet the canonized emission limit values.
This monitoring can be replaced by the Followed by a representative parameter, correlated with emissions. This correlation should be periodically confirmed by a measurement of emissions.
In other cases, grab samples are taken.
When the facility is equipped with an oxidant, compliance with the emission limit values NOx, methane and CO provided for in Article 34 of the Order of 2 February 1998 shall be checked once a year, on continuous and stable operation.
8 ° Ammonia, chlorine, hydrogen sulphide:
If the hourly flux of chlorine or hydrogen sulphide exceeds 1 Kg/h, the continuous emission measurement is performed.
The hourly flux is increased to 10 kg/h for ammonia.
9 ° Reduced sulphur compounds:
If the hourly flux of the sum of the reduced sulphur compounds is greater than 5 g/h on the one hand and if The odour concentration measured at the emission is greater than 100 000 UO/m³ on the other hand, the permanent emission measurement is carried out, unless the SO2 emissions are greater than 50 mg/Nm³.
10 ° Odour rate:
If the concentration Of odours is greater than 100 000 UO/m³, a quarterly measurement is carried out before and after the odour treatment device. The periodicity is annual if a representative and permanent measurement of the odour rate is carried out, for example, using an electronic nose. If the concentration of odours is strictly less than 100 000 UO/m³ and more than 5 000 UO/m³, a semi-annual measure shall be carried out. The periodicity shall be once every two years if a representative and permanent measurement of the odour rate is carried out in particular by using an electronic nose.
For any toxic or carcinogenic substance, including ammonia, and produced or used at more than 10 tonnes per year, the operator shall address the prefect no later than 31 May of the year An annual review of releases, chronic or accidental, in air, water and soil, regardless of the route, and in the waste disposed outside of the licensed facility.
A balance sheet of greenhouse gas emissions emitted by the classified facility and not covered by Article 46 of this Order shall be established annually And transmitted to the prefect when the annual emissions exceed the following values:
CO2: 10 000 tonnes;
CH4: 100 tonnes;
N2O: 20 tonnes;
CFC and HCFC: 0.5 tonnes.
I. -Operators of facilities discharging into the atmosphere more than:
200 kg/h of sulphur oxides;
200 kg/h of nitrogen oxides;
150 kg/h of organic compounds;
50 kg/h of dust;
50 kg/h inorganic compounds Chlorine gas;
50 kg/h hydrochloric acid;
25 kg/h fluorine and fluorinated compounds;
100 g/h lead and its compounds (expressed in Pb) or 500 g/h
(in the case of combustion plants consuming heavy fuel oil, this value is Range at 2000 g/h) provide for monitoring of air quality or deposition (for dust).
Samples, measurements and analyses are carried out according to the reference methods in accordance with section 45-II.
Number of points Measurement and the conditions under which measuring devices are installed and operated are set under the control of the inspection of classified installations.
Diffuse emissions are taken into account.
Participating operators An air quality measurement network that includes measurements of the pollutant may be exempt from this obligation if the existing network is able to properly monitor the effects of their releases.
II. -In order to allow better prevention and better monitoring of odour nuisance, operators of installations that emit a concentration of odor at the emission greater than 100 000 UO/m³ or which are the subject of numerous complaints from Olfactory discomfort set up an odour observatory, permanent or temporary, allowing:
-to follow an indication of disturbance or olfactory comfort perceived by the population in the vicinity of the installation, in accordance with Annex III;
- Either to qualify the evolution of the overall level of the olfactory impact of the installation
In the event of a risk of soil pollution, appropriate monitoring is implemented. The location of the pickup points, the frequency, and the type of analyses to be performed are fixed by the authorization order or by an additional order
The provisions of this Order shall apply to facilities whose authorization order will be issued more than one year after the publication of this Order and to the amendments Or extensions of existing installations subject to the same date of the procedures provided for in the second and third paragraph of Article 20 of the aforementioned Decree of 21 September
. Provisions of this Order shall apply according to the timetable set out in Annex IV.
For the provisions of Article 43 concerning noise, the implementing rules for new and existing installations shall be those of the order of 23 January 1997.
Authorizations for existing installations are made compatible, for the water sector, with the Provisions of the master plan for the development and management of water and the layout of water, where it exists.
The implementation of the provisions of this Order is subject to periodic evaluation by the Board of Classified Facilities. The latter shall examine any useful proposal for amendment of this Order, in particular in view of the adequacy of the limit values retained in Chapter IV in relation to the available processes and technologies and their evolution.
A N N E X E I
RESIDUAL WATERS
When the authorized daily maximum flow exceeds 100 m³ per day or 1/10 of the average flow Inter-annual within the meaning of Article L. 232-5 of the Rural Water Code, the authorisation order shall also set a limit to the monthly average daily rate and an instantaneous limit value.
The temperature of the effluent discharged is Below 30 ° C and their pH is between 5.5 and 8.5, 9.5 if alkaline neutralization.
The change in colour of the receiving environment, measured at a representative point of the mixing zone, does 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, also comply with the following provisions:
-do not result in a maximum temperature rise of 1.5 ° C for salmon waters, 3 ° C for cyprinid waters and 2 ° C for water Shellfish;
-do not induce a temperature greater than 21.5 ° C for salmon waters, at 28 ° C for cyprinid waters and at 25 ° C for water for the production of food water;
-maintain a pH between 6 and 9 For salmon and cyprinicolous waters and for bathing water, between 6.5 and 8.5 for water intended for the production of food water and between 7 and 9 for shellfish waters;
-not to cause an increase Greater than 30 % of the suspended solids and a variation greater than 10 % of the salinity for the shellfish waters.
Waste water discharged to the natural environment meets the following concentration limit values, depending on the flow Maximum permitted daily:
DBO5 (on non-decanted effluent): 100 mg/l if the maximum permitted daily flow does not exceed 15 kg/day; 30 mg/l beyond.
DCO (on non-decanted effluent): 300 mg/l if the maximum daily flow allowed does not exceed 50 kg/d; 125 mg/l beyond.
MEST: 100 mg/l if the maximum permitted daily flow does not exceed 15 kg/d; 35 mg/l above; 150 mg/l for lagoon treatment.
Different concentration limit values can be set By the authorization order in the following cases:
-where there is a limit value expressed as a specific pollution flow;
-when the installation treatment plant has a performance of at least 95 % for the DCO, the DBO5 and MEST;
-where the installation treatment plant has a performance at least 85 % for the COD, but the concentration exceeds 300 mg/l, and 90 % for DBO5 and MSEs, but without the concentration exceeding 100 Mg/l.
For facilities ensuring the treatment of corpses, waste or by-products of animal origin, excluding the treatment of feathers and duvets, and in general, installations providing for exclusive washing activities of By-products, specific flows do not exceed:
DBO5: 150 g/t raw materials;
DCO: 600 g/t raw materials;
MEST: 100 g/t raw materials.
Nitrogen and phosphorus fluxes comply with provisions
a) General provisions:
Nitrogen (global nitrogen including organic nitrogen, ammoniacal 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 facility's performance at the facility reaches at least 80 % for the new facility and 70 % for the new facility. Modified facilities.
Phosphorus (total phosphorus):
10 mg/l in monthly mean concentration when the maximum daily flow allowed is equal to or greater than 15 kg/day.
Different concentration limit values can be Fixed by the authorization order when the performance of the plant treatment plant reaches at least 90 % for phosphorus.
(b) Special provisions for discharges to the natural environment belonging to a sensitive area such as As defined in accordance with Article 6 of Decree No. 94-469 of 3 June 1994 on the collection and treatment of waste water referred to in Articles L. 2224-8 and L. 2224-10 of the General Code of Territorial
. Previous provisions, the authorization order, depending on the flow levels of the discharge and the characteristics of the receiving environment, imposes the following provisions for at least one of the two parameters:
Nitrogen (global nitrogen including nitrogen Organic, ammoniacal nitrogen, oxidized nitrogen):
15 mg/l in monthly mean concentration when the maximum daily flow allowed is equal to or greater than 150 kg/d;
10 mg/l in monthly mean concentration when daily flow Maximum allowed is equal to or greater than 300 kg/d.
Different concentration limit values may be set by the authorization order when the performance of the plant treatment plant reaches at least 80 % for Nitrogen.
Phosphorus (total phosphorus):
2 mg/l in monthly mean concentration when the maximum daily flow allowed is equal to or greater than 40 kg/day;
1 mg/l in monthly mean concentration when the maximum daily flow Authorized is greater than 80 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.
For Nitrogen, where the wastewater treatment process is a biological process, the provisions in the a and 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
SCANDAGE
1. "The term" Spreading " Any application of waste or effluent to or from agricultural soils.
Only waste or effluent that has an interest in soil or crop nutrition can be applied.
Nature, characteristics and quantities Waste or effluent intended for application shall be such that their handling and application shall not affect, directly or indirectly, the health of man and animals, the quality and the phytosanitary status of the crops, the quality Soil and aquatic environments, and that nuisance is minimized.
2. Application periods and quantities applied are adapted to:
-to provide input to soils or crops without exceeding Needs, taking into account inputs of any kind, including fertilizers, amendments, and culture media;
-to prevent prolonged stagnation on soils, runoff outside the spreading plots, rapid percolation ;
-to prevent the accumulation in the soil of substances that may have a long-term degradation of its structure or to present an ecotoxic hazard;
-to prevent soil clogging, especially by fat.
3. Application is prohibited:
-during periods when the ground is taken in mass by frost or heavy snow, except for solid waste;
-during periods of high rainfall and during periods when there is a risk Flooding;
-outside regularly worked land and grasslands or logged forests;
-on steep terrain, under conditions that would lead to runoff from the field of application;
-using Zero-sprinkling devices that produce fine fog when the effluent is likely to contain pathogenic microorganisms.
4. Subject to the requirements laid down in accordance with Article L. 1331-1 of the Public Health Code, the application of waste or effluent shall respect the minimum distances and time limits set out in the following table:
You Can refer to the table in OJ
No 89, 15/04/2003 page 6654 to 6662
You can view the table in OJ
No 89, 15/04/2003 page 6654 to 6662
Solid or unstabilized solid waste is buried as soon as possible, within 48 hours, to reduce odour nuisance and losses by volatilization.
Derogations from the obligation However, landfill may be granted for existing crops provided that they are not intended for direct human consumption.
5. Any application is subject to a preliminary study, included in the impact study, showing the safety (in the conditions of employment) and the agronomic interest of the effluent or waste, the ability of the soil to receive them, the spreading perimeter and The terms and conditions of its implementation.
This study justifies the compatibility of the application with identified environmental constraints or existing planning documents and is in accordance with the provisions of this Order and those that Resulting from other regulations in force.
This pre-study must include at least:
-the presentation of waste or effluent: origin, manufacturing processes, quantities and characteristics;
-representation Map to 1/25 000 of the study area and land application areas;
-the map representation, on an appropriate scale, of the land application plots and those excluded, specifying the grounds for exclusion ;
-the list of parcels retained with their cadastral reference;
-identification of the constraints associated with the natural environment or human activities within the study area and analysis of the nuisance that could result from the application ;
-a description of the characteristics of the soils, cropping systems, and crops considered within the study area;
-a soil analysis of the parameters listed in the following table, performed at a reference point, Representative of each homogeneous area;
You can consult the table in OJ
No 89, 15/04/2003 page 6654 to 6662
-justification for intake doses and application frequencies On the same parcel;
-the description of the technical procedures for implementing the application;
-the description of the procedures for monitoring the application and quality control of the effluent or waste applied;
-the Location, volume and characteristics of storage structures. The preliminary study shall be supplemented by the written agreement of the farmers of the plots for the implementation of the application under the conditions envisaged.
An alternative pathway for the disposal or recovery of solid or pasty waste Shall be provided for in the event of a temporary inability to comply with the provisions of this decree.
The prefect may call upon an independent body of the producer of waste or effluent and set up an agronomic monitoring device Applications for the preservation of soil, crop and product quality.
6. The pH of the effluent or waste is between 6.5 and 8.5. However, different values may be retained subject to favourable conclusions from the screening.
Waste or effluent must not be applied to soils with a pre-application pH of less than 6, except when The following conditions are simultaneously met:
-the soil pH is greater than 5;
-the nature of the waste or effluent can contribute to the pH of the soil at a value greater than or equal to 6.
7. Where wastes or effluents contain undesirable elements or substances or pathogens, the pre-study record must allow for the assessment of the safety of the waste in the prescribed conditions of
. Specifies the maximum concentration and maximum flux of the element, substance or pathogen considered, brought to the ground.
8. The intake dose is determined on the basis of:
-the type of crop and the realistic yield objective;
-the needs of the crops grown in major, secondary and micronutrient nutrients, all inputs combined;
- Levels of nutrients in the soil and in the waste or effluent and in other inputs;
-levels of unwanted elements or substances in waste or effluent;
-soil water status;
- Frequency of inputs in the same year or on a multi-year crop succession.
For nitrogen, these intakes (expressed as a global N), all origins, do not exceed the following values:
-on grasslands Natural, or on artificial meadows in place all year and in full production: 350 kg/ha/year;
-on other crops (except legumes): 200 kg/ha/yr;
-on pulse crops no nitrogen supply. The application of the effluents of the agri-food installations only dealing with materials of plant origin on alfalfa crops can, however, be authorised by the prefect under conditions laid down in the order for authorisation within the limits 200 kg/ha/yr of global nitrogen.
For crops other than grasslands and leguminous crops, intakes above 200 kg/ha/yr may be tolerated if the mineral nitrogen in the waste is less than 20 % of the total nitrogen, subject to:
-that the average aggregate nitrogen supply over five years, combined, does not exceed 200 kg/ha/year;
-that supplies of nitrogen by mineralization of organic nitrogen and other inputs do not exceed 200 kg/ha/year;
-to carry out nitrogen measurements in the soil exploitable by the roots at periods adapted to follow the fate of nitrogen in the soil and permit a manure plan adapted for the following crops;
-the opinion of the approved hydrogeologist in The risk to groundwater.
The final dose for solid or pasty waste is at most 3 kilograms of dry matter per square metre over a 10-year period, excluding land and lime.
9. Permanent waste or effluent storage structures are sized to deal with periods when the application is either impossible or prohibited by the prior study. All arrangements are made to ensure that storage devices do not cause disturbance or nuisance to the vicinity and do not cause water or soil pollution by runoff or infiltration. Spills in the natural environment of overflows of storage structures are prohibited. Open-air storage works are not permitted to access unauthorized third parties.
The temporary storage of waste, on land applications and without development work, is permitted only when the following five conditions are met: At the same time:
-the waste is solid and not fermentable, in the absence of it, the duration of the deposit is less than 48 hours;
-all precautions have been taken to prevent runoff on or off the plots Application or rapid percolation to groundwater or groundwater;
-the deposit shall respect the minimum isolation distances defined for the application in point 4, except for the distance from the housing or premises inhabited by the A third party that is always 100 meters. In addition, a distance of at least 3 metres from roads and ditches must be respected;
-the volume of the deposit is adapted to the reasoned fertilization of the receiving plots for the period of application considered;
-the maximum duration Must not exceed one year and the return to the same location cannot occur within three years.
10. An annual forecast application programme shall be drawn up, in agreement with the farmer, no later than one month before the start of the operations concerned. This program includes:
-the list of parcels or groups of parcels affected by the campaign, as well as the characterization of cropping systems (crops implanted before and after application, period of interculture) on these plots;
-a soil analysis of the parameters listed in Table 5-2 (characterisation of the agronomic value) selected on the basis of the preliminary study;
-a characterization of waste or effluent to be applied (quantities Forecast, rate of production, agronomic value, ...);
-specific recommendations for the use of waste or effluent (timing and doses of application by crop unit ...);
-identification of legal persons or Physical activity in the application of the application.
This forecast program is available for inspection of classified facilities. The prefectural decree provides for the transmission of this programme to the prefect before the start of the campaign.
11. A shelf-book, kept for a period of ten years, made available to inspection of classified facilities, must be maintained. It contains the following information:
-the quantities of effluent or waste applied per crop unit;
-application dates;
-the receiving plots and their surfaces;
-the cultures used;
-the context Weather during each application;
-all analytical results performed on soils and on waste or effluent, with dates of sampling and measurements and their location;
-identification of individuals
producer of waste or effluent must be able to justify at any time the location of the waste or effluent produced (storage, temporary storage, transport Or application) in reference to their production period and to the analyses performed.
12. A balance sheet is prepared annually. This document includes:
-the receiving plots;
-a qualitative and quantitative balance sheet of the waste or effluent applied;
-the operation of the application book showing the quantities of nutrients and nutrients Adverse effects on each crop unit and the results of soil analyses;
-reports of smoking on reference plots representative of each type of soil and culture systems, as well as the advice of
-the possible updating of the data collected during the initial study.
A copy of the balance sheet is addressed to the prefect and the farmers concerned.
13. Effluents or wastes are analyzed in the first year of application or when changes in processes or treatments are likely to affect their quality.
These analyses are for:
-the dry matter rate;
-the elements of characterisation of the agronomic value among those mentioned in point 5;
-the chemical elements and substances likely to be present in the waste or effluent in the light of the preliminary study;
-the pathogens
Outside the first year of application, the effluent or waste is analyzed periodically.
The nature and periodicity of the analyses are determined by the authorization order.
14. Sampling and analyses of effluents or wastes, including leachates, are carried out using standardized methods, where they exist. Otherwise, these methods are defined by the laboratory.
15. The volume of effluent being applied is measured either by totalizing hourly meters which are equipped with the backflow pumps, either by direct measurement or by any other equivalent process.
16. The authorization decree defines the conditions under which the application is to be applied. In particular, it provides for the establishment of a contract binding the producer of waste or effluent to the provider carrying out the application and contracts binding the producer of waste or effluent to farmers operating the land. These contracts define the commitments of each and their durations. The Order also sets out:
-the possible treatment of waste or effluent;
-maximum levels of unwanted substances and substances and pathogens present in effluents or wastes ;
-the methods of application;
-the maximum annual quantity of elements and unwanted substances and fertilizing materials applied per hectare;
-the application bans;
-the technical requirements applicable to the Storage devices and temporary depots;
-the nature of the information to be included in the application specification referred to in point 10;
-the transmission to the prefect of the annual balance sheet and, if applicable, of the estimated programme;
-la Frequency of analyses on waste or effluent and their nature, the monitoring procedures and the conditions under which they are transmitted to users and to the inspection of classified installations responsible for the control of such operations ;
-the frequency and nature of soil testing.
As required, the order requires periodic monitoring of groundwater quality, from existing sampling points or through the development of piezometers, on or in Outside the spreading zone according to the local hydrogeological context.
A N N E X E I I I
METHOD OF CALCULATION OF AN LOAN INDICE
The index of discomfort is a function of two sub-indices: Frequency and index of nuisance. The index of discomfort varies on a scale graded from 0 to 10, the level 10 corresponding to the maximum discomfort.
To overcome the influence of the wind direction, the Ifreq frequency index used represents the frequency of perception of odors The site of an observer if the observer was constantly under the wind of the site. It is defined as follows:
Ifreq = 10 x Nperc/Nmax with Nmax = P x Nobs
Nmax = theoretical maximum number of observations with scent perception from the site.
Nobs = number of cases Olfactory active during the observation period.
Nperc = number of observations with scent perception from installation.
P = frequency of occurrence of wind directions placing the observer under the wind of the site.
The olfactory nuisance index is defined as follows:
Inuisance = [(0 x N1) + (1/3 x N2) + (2/3 N3) + (1 x N4)]/(N1 + N2 + N3 + N4)
N1 = number of observations describing non-troublemose odours
N2 = number of observations describing unhindered odours from the installation.
N3 = number of observations describing annoying odours originating from the transmitter site.
N4 = number of observations describing Very annoying odours from the transmitter site
The discomfort index is defined as follows:
Igêne = (Inuisance x Ifreq) ¹/²
The Igêne value compared to the following scale gives an indication of The importance of the nuisance generated by the installation.
-if Igêne is less than 2.5, olfactory comfort is good;
-if Igêne is between 2.5 and 5, olfactory comfort is fair;
-if Igêne is between 5 and 7.5, the Olfactory comfort is degraded;
-if Igêne is greater than 7.5, olfactory comfort is poor.
A N N E X E I V
APPLICATION SCHEDULE
TO EXISTING FACILITIES
Facilities Shall be brought into conformity with the provisions of this Order within the following periods, counted from the publication of this Order in the Official Journal of the French Republic:
You may Consult the table in OJ
No 89, 15/04/2003 page 6654 to 6662
Done at Paris, February 12, 2003.
For the Minister by delegation:
The Director of the
pollution and risk prevention,
delegate to major hazards,
P. Vesseron
