Key Benefits:
Minister of Ecology and Sustainable Development,
In view of Council Directive 90/667 of 27 November 1990 amending Directive 90/425, laying down the health rules relating to The disposal and processing of animal waste;
In view of 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 consumption Human;
In view of the Council Directive of 15 July 1975 on waste (75/442/EEC), as amended by the Council Directive of 18 March 1991 (91/156/EEC);
In view of the Council Directive of 12 June 1986 on the protection of The environment, and in particular the soil, in the use of sewage sludge in agriculture (86/278/EEC);
Given the environmental code;
Having regard to Decree No. 77-1133 of 21 September 1977, as amended for the purposes of Act No. 76-663 of the 19 July 1976 on classified installations and Title I of Law No. 64-1245 of 16 December 1964 on the regime and distribution of water and the control of their pollution;
In the light of Decree No. 91-1283 of 19 December 1991 on Quality objectives assigned to watercourses, stream sections, canals, lakes or ponds and the waters of the sea within the territorial limits;
Given Decree No. 92-1042 of 24 September 1992 on the application of Article 5 of Act No. 92-3 of the 3 January 1992 on water and water management and management schemes;
In view of the Decree of 30 December 1991 on the processing of animal waste and the production of feed for animals of animal
; The Board of Governors of the facilities classified as of June 27, 2002,
Stop:
For the purposes of this Order, installation means:
-the buildings in which the operations of Receipt and storage of raw materials;
-Annexes: waste storage and treatment devices, truck wash stations used for the transport of meat, corpses, debris or animal origin.
The installation must be installed:
-at least 200 metres from the homes occupied by third parties or locals 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;
-at least 35 Metres of wells and boreholes at the site, sources, open-flow aqueducts, any underground or semi-buried facilities used for the storage of drinking water, shorelines, shorelines of the Watercourses;
-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 the shellfish areas The
lot of the transport vehicles of meat, corpses, debris or 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, 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:
(designation of installation)
Deposit of waste of animal origin
subject to authorisation under Article L. 512-2
of the code of Environment
Prefectural authorization (n °) of (date)
(social reason) and (operator's address)
The organization of vehicle traffic within the site shall be designed to ensure that no soiled vehicle leaves the site without proper washing.
The traffic plan within the 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 outfalls and their periphery are the subject of special care (planting, engazing, etc.).
The soil of the Means of circulation and garage other than the roads connected with the parking of vehicles after washing and disinfection shall be watertight and equipped so 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 protect the environment such as filters, neutralization products, inhibitory liquids, absorbent products
The operator shall make all arrangements Necessary in the design, construction and operation of installations to limit the risks of accidental pollution of air, water or soil.
Reception areas and storage facilities must be under closed building to limit Odour clearances in the vicinity of the facility, including the installation of automatic access doors.
These areas must also be watertight and managed in such a way as to dispose of meat juices, corpses, etc. Debris or derived from animal origin shall not reach the natural environment directly and shall be collected and treated in accordance with the provisions of Article 27
The storage facilities for meat, corpses, debris, or animal origin must be constructed in impermeable, shock-resistant materials To clean and disinfect, on all their height.
The soil shall be watertight, resistant to the passage of equipment and vehicles allowing the unloading of flesh, corpses, debris or animal origin and designed to facilitate Drainage of drip juice and cleaning water to collection facilities.
Premises should be properly lit and allow for the protection of waste from the weather and heat.
The storage time must not exceed 24 hours before leaving the site.
This delay can be extended if all the flesh, corpses, debris Or derived from animal origin is maintained at a temperature less than + 7 ° C.
The capacity of the premises must be compatible with the maximum storage time and allow a 24-hour increase in the time limit.
All storage facilities for raw materials must be kept in a good state of cleanliness and are cleaned at least twice
The installation must have adequate equipment to clean and disinfect the containers or containers in which the animal waste is received, and the vehicles in which they are transported.
The Containers, containers and vehicles used for the transport of animal waste must be cleaned and washed after each use and disinfected regularly and at least once a week (interior and exterior).
The wheels of the vehicles In particular, transport must be disinfected after each use.
The collection and storage of flesh, corpses, debris or animal origin must be carried out in watertight containers or containers with liquids and closed Transport time.
Any storage of a liquid capable of creating water or soil pollution and in particular The storage unit of the waters having been in contact with meat, corpses, debris or animal origin is associated with a holding capacity whose volume is at least equal to the greater of the following two values:
100 % of the Capacity of the largest reservoir.
50 % of the total capacity of the associated tanks.
This provision is not applicable to waste water treatment tanks.
For storage of containers of lower unit capacity 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 the total capacity of drums;
-in other cases, 20 % of total barrels capacity;
- In all cases, 800 litres minimum or equal to the total capacity of less than 800 litres.
The holding capacity is impervious to the products that it may contain and is resistant to 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, as well as 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; Security data set out in the Labour Code to meet this obligation.
Within the authorized classified installation, drums, tanks and other packaging shall bear the names of the products in very legible characters and Hazard symbols in accordance, where applicable, to the regulation of the labelling of dangerous chemical substances and preparations
The effluent collected on the site belongs to one of the three categories
-uncontaminated stormwater;
-soiled waters and waters that have been in contact with meat, corpses, debris or animal origin or with surfaces soiled by these materials;
-other waters (par. Example, wash-water including wash-water where appropriate, purging waters, sluices ...).
The different Effluents are treated as follows:
-the uncontaminated stormwater is discharged to the natural environment or to the storm system serving the facility, if it exists;
-the waters having been in contact with flesh, corpses, Debris or exits of animal origin or surfaces which may be soiled by these materials shall be treated in accordance with the provisions of Article 27;
-other waters shall be purified when processing is necessary for the Respect for the limit values imposed on the release and set out in Appendix I.
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 elements, a lump sum value of not less than 5 m³ /t of meat, corpses, waste or derived animal origin shall be 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 18
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 incoming raw materials 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 provisions of the Water Management and Management Master Plan, where it exists. Each sampling point in the ground or watercourse shall be equipped with a totalizing time meter.
The volumes consumed shall be recorded daily if the flow rate is likely to exceed 100 m³ /d and weekly if That flow rate is lower; they are recorded in a computerized register kept available to the inspector of classified installations.
When drilling in tablecloth, all provisions shall be taken to prevent the communication of separate water bodies, unless explicit authorisation is given in the authorisation order, and to prevent Any introduction of surface pollution, including appropriate development.
In the event of cessation of use of drilling, the operator shall take appropriate measures for the sealing or sealing of the work in order to avoid pollution Underground water bodies.
The completion of any new drilling or the decommissioning of a borehole is brought to the attention of the prefect with all the assessment elements of the hydrogeological impact
Processing conditions and emission limit values are Set out in the authorization order on the basis of the use of the best available technologies at an acceptable economic cost and the particular characteristics of the environment.
The collection piping of the effluent that is polluted or likely to be contaminated is watertight and resists the physical and chemical action of the products they are capable of 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 ...
With the exception of accidental cases where the safety of persons or installations would be It is prohibited to establish direct links between the effluent collection systems for treatment or destruction and the receiving environment.
Rejection points in the natural environment are as small as possible. Rejection structures shall permit the release of effluent to the receiving environment
La Dispersion of odours in the ambient air of the reception and storage facilities of the raw material must be limited as much as possible:
-by storing the flesh, corpses, debris or animal origin according to the provisions of the Section 13;
-ensuring the permanent closure of the reception and storage building of the flesh, corpses, debris or animal origin;
-by proper cleaning and disinfection of the premises.
The following provisions apply to soiled waters and waters that have been in contact with the flesh, corpses, debris Or derived from animal origin or with surfaces soiled by such materials.
Effluents may be treated on-site or at an authorized plant.
I.-Depots of flesh, corpses, debris, or animal origin, including destruction Is made regulatory mandatory must meet one of the following obligations:
-be equipped with a device to ensure the absence of liquid discharge;
-to ensure that liquid effluents are autoclaved at 133 ° C for 20 minutes under pressure of 3 bars without interruption and be equipped with a filtration device to hold particles of a size greater than 10 µ m or any other device deemed equivalent, so as to respect the Discharge standards set out in Annex I.
II. -Deposits of meat, corpses, debris or animal origin, the destruction of which is not legally binding, shall comply with the emission standards set out in Annex I.
I. -For installations referred to in paragraph I of Article 27, sludge and waste from the wastewater treatment plant shall be treated by a incineration plant or co-incineration plant directly or after Dehydration.
II. -For installations referred to in paragraph II of Article 27, 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 treatment of equivalent effectiveness. Sludge from water treatment plants may be applied in accordance with the provisions laid down in Annex II.
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.
The transport of all other waste, residues and by-products must Be insured in dedicated and watertight vehicles.
Before departure, vehicles that have been circulated on a soiled area must be properly cleaned.
Wastes that cannot be recovered shall be disposed of in facilities regulated for this purpose under Book V of the Environmental Code under conditions permitting To ensure the protection of the environment; the operator is in a position to justify the removal on request of the inspection of classified installations. It shall 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 air is prohibited.
The authorization order sets out the conditions for the disposal of the various wastes generated by the facility and, in particular, The characteristics and maximum quantities of solid waste that the operator is authorized to store.
Emissions Sound of the installation comply with the provisions of the decree of 23 January 1997 concerning the limitation of noise emitted in the environment by installations classified for the protection of the environment.
The installation is constructed, equipped and operated in such a way that its operation cannot be the source of mechanical vibrations that may Endanger the health or safety of the neighbourhood or constitute a nuisance to the neighbourhood.
The vibrations issued comply with the technical rules annexed to the circular of 23 July 1986 concerning mechanical vibrations issued in The environment by classified facilities. Measurements are made according to the methodology defined by this circular.
In the event of a risk of soil pollution, a 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 take place 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 Decree of 21 September 1977.
For existing classified installations, the Provisions of this Order shall apply according to the timetable set out in Annex III.
For the provisions of Article 33 concerning noise, the implementing rules for new and existing classified installations shall be those of the order January 23, 1997.
The authorizations for existing facilities are made compatible for the water sector. With the provisions of the proposed water management and management scheme and the water management scheme, 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 maximum allowable daily flow exceeds 100 m³ per day or 1/10 of the average throughput Inter-annual within the meaning of s. L. 232-5 of the rural code of the watercourse, the authorization decree also sets a limit to the monthly average daily flow rate and a instantaneous limit value.
The temperature of the effluent discharged is less than 30 ° C and their pH is Between 5.5 and 8.5, 9.5 if alkaline neutralization occurs.
The colour change 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 daily permitted:
DBO5 (on non-decanted effluent): 100 mg/l if the maximum permitted daily flow does not exceed 15 kg/day; 30 mg/l above;
DCO (on non-decanted effluent): 300 mg/l if the maximum daily flow allowed does not exceed 50 Kg/day; 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:
-when the installation treatment plant has a performance of at least 95 % for the COD, the DBO5 and the MEST;
-when the installation treatment plant has at least one performance 85 % for the COD, without however the concentration exceeds 300 mg/l, and 90 % for DBO5 and MSEs, but without the concentration exceeding 100 mg/l.
The specific flows, when determined, 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 the following 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/day.
Different concentration limit values can Be fixed by the authorization order when the facility's performance at the facility reaches at least 80 % for nitrogen for new facilities and 70 % for 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 may be set by the authorization order when the performance of the Installation treatment plant reaches at least 90 % for phosphorus.
(b) Special provisions for discharges into the natural environment belonging to a sensitive area as defined in accordance with Article 6 of Decree No 94-469 of the 3 June 1994 concerning the collection and treatment of waste water referred to in Articles L. 2224-8 and L. 2224-10 of the General Code of Territorial Communities.
In addition to the previous provisions, the authorisation order, according to the levels of Flow of discharge and characteristics of the receiving environment, impose the following provisions for at least one of the two parameters.
Nitrogen (global nitrogen including organic nitrogen, ammoniacal nitrogen, oxidized nitrogen):
15 mg/l concentration Monthly mean when the maximum daily flow allowed is equal to or greater than 150 kg/day;
10 mg/l in monthly mean concentration when the maximum daily flow allowed equals or exceeds 300 kg/day.
Limit values Different concentrations may be determined by the authorization order when the facility's performance at the facility reaches at least 80 % for nitrogen.
Phosphorus (total phosphorus):
2 mg/l in average concentration Monthly when the maximum daily flow allowed is 40 kg/day;
1 mg/l in monthly mean concentration when the maximum daily flow allowed is greater than 80 kg/day.
Concentration limit values May be fixed by the authorization order when the performance of the installation treatment plant reaches at least 90 % for phosphorus.
For nitrogen, where the treatment process implemented is a process The provisions in the a and b are complied with 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 pursuant to 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 view the table in OJ
No 89, 15/04/2003 page 6662 to 6669
You can view the table in OJ
No 89, 15/04/2003 page 6662 to 6669
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 6662 to 6669
-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 surface or ground slicks;
-the deposit follows the minimum isolation distances defined for the application in point 4 except for the distance from the residential or local area 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 planted 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 the 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 Unwanted on each crop unit and the results of the soil analyses;
-the manure budgets on reference plots representative of each type of soil and cropping 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 are carried out using standardized methods, where they exist. Otherwise, these methods are defined by the laboratory.
15. The volume of effluent discharged 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
APPLICATION SCHEDULE
TO EXISTING FACILITIES
Existing installations must be installed 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 can consult the table in the OJ
n ° 89, 15/04/2003 page 6662 to 6669
Done at Paris, February 12, 2003.
For the Minister by delegation:
The Director of Prevention
Pollution and risk,
delegate to major risks,
P. Vesseron
