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Regulation (EC) No 2003/2003 of the European Parliament and of the Council of 13 October 2003 relating to fertilisers (Text with EEA relevance)
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The oil retention of the fertiliser, which must first have undergone two thermal cycles of a temperature ranging from 25 to 50 °C and conforming with the provisions of part 2 of section 3. of this Annex, must not exceed 4 % by mass.
The percentage by mass of combustible material measured as carbon must not exceed 0,2 % for fertilisers having a nitrogen content of at least 31,5 % by mass and must not exceed 0,4 % for fertilisers having a nitrogen content of at least 28 % but less than 31,5 % by mass.
A solution of 10 g of fertiliser in 100 ml of water must have a pH of at least 4.5.
Not more than 5 % by mass of the fertiliser must pass through a 1 mm mesh sieve and not more than 3 % by mass must pass through a 0,5 mm mesh sieve.
The maximum chlorine content is set at 0,02 % by mass.
Heavy metals should not be added deliberately, and any traces which are incidental to the production process should not exceed the limit fixed by [F1this Regulation].
Textual Amendments
F1Words in Annex 3 para. 1.6 substituted (31.12.2020) by The Fertilisers and Ammonium Nitrate Material (Amendment) (EU Exit) Regulations 2019 (S.I. 2019/601), regs. 1(2), 5(22); 2020 c. 1, Sch. 5 para. 1(1)
The copper content shall not be higher than 10 mg/kg.
No limits are specified for other heavy metals.
The test must be carried out on a representative sample of fertiliser. Before being tested for resistance to detonation, the whole mass of the sample is to be thermally cycled five times complying with the provisions of part 3 in section 3. of this Annex.
The fertiliser must be subjected to the test of resistance to detonation in a horizontal steel tube under the following conditions:
seamless steel tube,
Tube length: 1 000 mm at least,
Nominal external diameter: 114 mm at least,
Nominal wall thickness: 5 mm at least,
Booster: the type and mass of the booster chosen should be such as to maximise the detonation pressure applied to the sample in order to determine its susceptibility to the transmission of detonation,
Test temperature: 15-25 °C,
Witness lead cylinders for detecting detonation: 50 mm diameter and 100 mm high
placed at 150 mm intervals and supporting the tube horizontally. The test is to be carried out twice. The test is deemed conclusive if in both tests one or more of the supporting lead cylinders is crushed by less than 5 %.
This document defines the procedures for the application of thermal cycles prior to the execution of the oil retention test for straight ammonium nitrate fertilisers of high nitrogen content and of the test on the resistance to detonation for both, straight and compound ammonium nitrate fertiliser of high nitrogen content.
The methods of the closed thermal cycles as described in this section are regarded as simulating sufficiently the conditions to be taken into account within the scope of application of title II, chapter IV, however, these methods may not necessarily simulate all conditions arising during transport and storage;
This procedure is for thermal cycling prior to determining the oil retention of the fertiliser.
In an Erlenmeyer flask, heat the sample from ambient temperature to 50 °C and maintain at this temperature for a period of two hours (phase at 50 °C). Thereupon cool the sample until a temperature of 25 °C is achieved and maintain at that temperature for two hours (phase at 25 °C). The combination of the successive phases at 50 °C and 25 °C forms one thermal cycle. After being subjected to two thermal cycles, the test sample is held at a temperature of 20 ± 3 °C for the determination of the oil retention value.
Normal laboratory apparatus, in particular:
water baths thermostated at 25 (± 1) and 50 (± 1) °C respectively,
Erlenmeyer flasks with an individual capacity of 150 ml.
Put each test sample of 70 (± 5) grams into an Erlenmeyer flask which is then sealed with a stopper.
Move each flask every two hours from the 50 °C bath to the 25 °C bath and vice versa.
Maintain the water in each bath at constant temperature and keep in motion by rapid stirring to ensure the water level comes above the level of the sample. Protect the stopper from condensation by a foam rubber cap.
This procedure is for thermal cycling prior to the execution of the detonability test.
In a watertight box heat the sample from ambient temperature to 50 °C and maintain at this temperature for a period of one hour (phase at 50 °C). Thereupon cool the sample until a temperature of 25 °C is achieved and maintain at that temperature for one hour (phase at 25 °C). The combination of the successive phases at 50 °C and 25 °C forms one thermal cycle. After being subjected to the required number of thermal cycles, the test sample is held at a temperature of 20 ± 3 °C pending the execution of the detonability test.
A water bath, thermostated in a temperature range of 20 to 51 °C with a minimum heating and cooling rate of 10 °C/h, or two water baths, one thermostated at a temperature of 20 °C, the other at 51 °C. The water in the bath(s) is continuously stirred; the volume of the bath should be large enough to guarantee ample circulation of the water.
A stainless steel box, watertight all around and provided with a thermocouple in the centre. The outside width of the box is 45 (± 2) mm and the wall thickness is 1,5 mm (see Figure 1). The height and length of the box can be chosen to suit the dimensions of the water bath, e.g. length 600 mm, height 400 mm.
Place a quantity of fertilisers sufficient for a single detonation into the box and close the cover. Place the box in the water bath. Heat the water to 51 °C and measure the temperature in the centre of the fertiliser. One hour after the temperature at the centre has reached 50 °C cool the water. One hour after the temperature at the centre has reached 25 °C heat the water to start the second cycle. In the case of two water baths, transfer the box to the other bath after each heating/cooling period.
Figure 1
This document defines the procedure for the determination of oil retention of straight ammonium nitrate fertilisers of high nitrogen content.
The method is applicable to both prilled and granular fertilisers which do not contain oil-soluble materials.
Oil retention of a fertiliser: the quantity of oil retained by the fertiliser determined under the operating conditions specified, and expressed as a percentage by mass.
Total immersion of the test portion in gas oil for a specified period, followed by the draining away of surplus oil under specified conditions. Measurement of the increase in mass of the test portion.
Gas oil
:
5 mPas at 40 °C
:
0,8 to 0,85 g/ml at 20 °C
:
≤ 1,0 % (m/m)
:
≤ 0,1 % (m/m)
Ordinary laboratory apparatus, and:
Balance, capable of weighing to the nearest 0,01 gram.
Beakers, of capacity 500 ml.
Funnel, of plastic materials, preferably with a cylindrical wall at the upper end, diameter approximately 200 mm.
Test sieve, aperture 0,5 mm, fitting into the funnel (5.3).
Note: The size of the funnel and sieve is such as to ensure that only a few granules lie one above another and the oil is able to drain easily.U.K.
Filter paper, rapid filtering grade, creped, soft, mass 150 g/m2.
Absorbent tissue (laboratory grade).
Textual Amendments
If the quantity of gas oil retained in the portion is found to be greater than 2 grams, place the portion on a fresh set of filter papers and repeat the rolling procedure, lifting the corners in accordance with section 6.4 (two times eight circular movements, lifting once). Then reweigh the portion.
The oil retention, from each determination (6.1) expressed as a percentage by mass of the sieved test portion, is given by the equation:
where:
m1 is the mass, in grams, of the sieved test portion (6.2),
m2 is the mass, in grams, of the test portion according to section 6.4 or 6.5 respectively as the result of the last weighing.
Take as the result the arithmetic mean of the two individual determinations.
This document defines the procedure for the determination of the combustible content of straight ammonium nitrate fertilisers of high nitrogen content.
The carbon dioxide produced by inorganic fillers is removed in advance with an acid. The organic compounds are oxidised by means of a chromic acid/sulphuric acid mixture. Carbon dioxide formed is absorbed in a barium hydroxide solution. The precipitate is dissolved in a solution of hydrochloric acid and measured by back-titration with sodium hydroxide solution.
Weigh out 15 grams of barium hydroxide [Ba(OH)2. 8H2O], and dissolve completely in hot water. Allow to cool and transfer to a one-litre flask. Fill up to the mark and mix. Filter through a pleated filter paper.
filter crucible with a plate of sintered glass and a capacity of 15 ml; plate diameter: 20 mm; total height: 50 mm; porosity 4 (pore diameter from 5 to 15 μm),
600-ml beaker.
Absorption tube A about 200 mm long and 30 mm in diameter filled with soda lime (3.9) kept in place by fibreglass plugs.
500-ml reaction flask B with side arm and a round bottom.
Vigreux fractionating column about 150 mm long (C').
Double-surface condenser C, 200 mm long.
[F2Dreschel bottle D acting as a trap for any excess of acid which may distil over.]
Ice bath E to cool the Drechsel bottle.
Two absorption vessels F1 and F2, 32 to 35 mm in diameter, the gas distributor of which comprises a 10 mm disc of low-porosity sintered glass.
Suction pump and suction regulating device G comprising a T-shaped glass piece inserted into the circuit, the free arm of which is connected to the fine capillary tube by a short rubber tube fitted with a screw clamp.
Caution: The use of boiling chromic acid solution in an apparatus under reduced pressure is a hazardous operation and requires appropriate precautions.U.K.
Weigh approximately 10 grams of ammonium nitrate to the nearest 0,001 grams.
[F2Place the sample for analysis in the reaction flask B. Add 100 ml of H 2 SO 4 (3.2). The prills or granules dissolve in about 10 minutes at ambient temperature. Assemble the apparatus as indicated in the diagram: connect one end of the absorption tube (A) to the nitrogen source (4.2) via a non-return flow device containing a pressure of 667 to 800 Pa and the other end to the feed tube which enters the reaction flask. Place the Vigreux fractionating column (C′) and the condenser (C) with cooling water supply in position. Adjust the nitrogen to provide a moderate flow through the solution, bring the solution to boiling point and heat for two minutes. At the end of this time there should be no more effervescence. If effervescence is seen, continue heating for 30 minutes. Allow solution to cool for at least 20 minutes with the nitrogen flowing through it.]
Complete assembly of the apparatus as indicated in the diagram by connecting the condenser tube to the Drechsel bottle (D) and the bottle to the absorption vessels F1 and F2. The nitrogen must continue to pass through the solution during the assembly operation. Rapidly introduce 50 ml of barium hydroxide solution (3.4) into each of the absorption vessels (F1 and F2).
Bubble a stream of nitrogen through for about 10 minutes. The solution must remain clear in the absorbers. If this does not happen, the carbonate removal process must be repeated.
After withdrawing the nitrogen feed tube, rapidly introduce 20 grams of chromium trioxide (3.1) and 6 ml of silver nitrate solution (3.3) via the side arm of the reaction flask (B). Connect the apparatus to the suction pump and adjust the nitrogen flow so that a steady stream of gas bubbles passes through the sintered-glass absorbers F1 and F2.
Heat the reaction flask (B) until the liquid boils and keep it boiling for one and a half hours(1). It may be necessary to adjust the suction-regulating valve (G) to control the nitrogen flow since it is possible that the barium carbonate precipitated during the test may block the sintered-glass discs. The operation is satisfactory when the barium hydroxide solution in the absorber F2 remains clear. Otherwise repeat the test. Stop heating and dismantle the apparatus. Wash each of the distributors (3.10) both inside and outside to remove barium hydroxide and collect the washings in the corresponding absorber. Place the distributors one after the other in a 600-ml beaker which will subsequently be used for the determination.
Rapidly filter under vacuum firstly the contents of absorber F2 and then of absorber F1 using the sintered-glass crucible. Collect the precipitate by rinsing the absorbers with water (3.10) and wash the crucible with 50 ml of the same water. Place the crucible in the 600-ml beaker and add about 100 ml of boiled water (3.10). Introduce 50 ml of boiled water into each of the absorbers and pass nitrogen through the distributors for five minutes. Combine the water with that from the beaker. Repeat the operation once to ensure that the distributors are rinsed thoroughly.
Add five drops of phenolphthalein (3.8) to the contents of the beaker. The solution becomes red in colour. Add hydrochloric acid (3.5) drop by drop until the pink colour just disappears. Stir the solution well in the crucible to check that the pink colour does not reappear. Add five drops of bromphenol blue (3.7) and titrate with hydrochloric acid (3.5) until the solution turns yellow. Add a further 10 ml of hydrochloric acid.
Heat the solution to boiling point and continue boiling for a maximum of one minute. Check carefully that no precipitate remains in the liquid.
Allow to cool and back titrate with the sodium hydroxide solution (3.6).
Carry out a blank test following the same procedure and using the same quantities of all reagents.
The content of combustible ingredients (C), expressed as carbon, as a percentage by mass of the sample, is given by the formula:
where:
=
the mass in grams of the test portion,
=
the total volume in ml of 0,1 mol/l hydrochloric acid added after the change in colour of the phenolphthalein,
=
the volume in ml of the 0,1 mol/l sodium hydroxide solution used for back titration.
Figure 2
This document defines the procedure for measuring the pH value of a solution of a straight ammonium nitrate fertiliser of high nitrogen content.
Measurement of the pH of an ammonium nitrate solution by means of a pH meter.
Distilled or demineralised water, free from carbon dioxide.
Dissolve 3,40 ± 0,01 grams of potassium dihydrogen orthophosphate (KH2PO4) in approximately 400 ml of water. Then dissolve 3,55 ± 0,01 grams of disodium hydrogen orthophosphate (Na2HPO4) in approximately 400 ml of water. Transfer the two solutions without loss into a 1 000-ml graduated flask, make up to the mark and mix. Keep this solution in an airtight vessel.
Dissolve 10,21 ± 0,01 grams of potassium hydrogen phthalate (KHC8O4H4) in water, transfer without loss into a 1 000-ml graduated flask, make up to the mark and mix.
Keep this solution in an airtight vessel.
pH meter, equipped with glass and calomel electrodes or equivalent, sensitivity 0,05 pH unit.
Calibrate the pH meter (4) at a temperature of 20 (± 1) °C, using the buffer solutions (3.1), (3.2) or (3.3). Pass a slow stream of nitrogen onto the surface of the solution and maintain this throughout the test.
Pour 100,0 ml of water onto 10 (± 0,01) grams of the sample in a 250 ml beaker. Remove the insolubles by filtering, decanting or centrifuging the liquid. Measure the pH value of the clear solution at a temperature of 20 (± 1) °C according to the same procedure as for the calibration of the meter.
Express the result in pH units, to the nearest 0,1 unit, and state the temperature used.
This document defines the procedure for the test sieving of straight ammonium nitrate fertilisers of high nitrogen content.
The test sample is sieved on a nest of three sieves, either by hand or by mechanical means. The mass retained on each sieve is recorded and the percentage of material passing the required sieves are calculated.
Calculate the percentage in the receiver (i.e. < 0,5 mm): A %
Calculate the percentage retained on the 0,5 mm sieve: B %
Calculate the percentage passing 1,0 mm, i.e. (A + B) %
The sum of the fraction masses should be within 2 % of the initial mass taken.
Report the mean of the two values obtained for A on the one hand and for A + B on the other.
This document defines the procedure for the determination of the chlorine content (as chloride ion) of straight ammonium nitrate fertilisers with a high nitrogen content.
Chloride ions dissolved in water are determined by potentiometric titration with silver nitrate in an acidic medium.
Distilled or demineralised water, free from chloride ions.
Take 5,00 ml and 10,00 ml of the standard reference potassium chloride solution (3.6) and place in two low-form beakers of convenient capacity (for example 250 ml). Carry out the following titration of the contents of each beaker.
Add 5 ml of the nitric acid solution (3.2), 120 ml of the acetone (3.1) and sufficient water to bring the total volume to about 150 ml. Place the rod of the magnetic stirrer (4.3) in the beaker and set the stirrer in motion. Immerse the silver electrode (4.1) and the free end of the bridge (4.2) in the solution. Connect the electrodes to the potentiometer (4.1) and, after verifying the zero of the apparatus, note the value of the starting potential.
Titrate, using the microburette (4.4), adding initially 4 or 9 ml respectively of the silver nitrate solution corresponding to the standard reference potassium chloride solution used. Continue the addition in 0,1 ml portions for the 0,004 mol/l solutions and in 0,05 ml portions for the 0,1 mol/l solutions. After each addition, await the stabilisation of the potential.
Record the volumes added and the corresponding values of the potential in the first two columns of a table.
In a third column of the table, record the successive increments (Δ1E) of the potential E. In a fourth column, record the differences (Δ2E) positive or negative, between the potential increments (Δ1E). The end of the titration corresponds to the addition of the 0,1 or 0,05 ml portion (V1) of the silver nitrate solution which gives the maximum value of Δ1E.
In order to calculate the exact volume (Veq) of the silver nitrate solution corresponding to the end of the reaction, use the formula:
where:
V0 is the total volume, in ml, of the silver nitrate solution immediately lower than the volume which gives the maximum increment of Δ1E,
V1 is the volume, in ml, of the last portion of the silver nitrate solution added (0,1 or 0,05 ml),
b is the last positive value of Δ2E,
B is the sum of the absolute values of the last positive values of Δ2E and the first negative value of Δ2E (see example in Table 1).
Carry out a blank test and take account thereof when calculating the final result.
The result V4 of the blank test on the reagents is given, in ml, by the formula:
where:
V2 is the value, in ml, of the exact volume (Veq) of the silver nitrate solution corresponding to the titration of 10 ml of the potassium chloride standard reference solution used,
V3 is the value, in ml, of the exact volume (Veq) of the silver nitrate solution corresponding to the titration of 5 ml of the potassium chloride standard reference solution used.
The blank test can at the same time serve as a check that the apparatus is functioning satisfactorily and that the test procedure is being implemented correctly.
Take a portion of sample in the range 10 to 20 grams and weigh to the nearest 0,01 gram. Transfer quantitatively to a 250-ml beaker. Add 20 ml of water, 5 ml of nitric acid solution (3.2), 120 ml of acetone (3.1) and sufficient water to bring the total volume to about 150 ml.
Place the rod of the magnetic stirrer (4.3) in the beaker, place the beaker on the stirrer and set the stirrer in motion. Immerse the silver electrode (4.1) and the free end of the bridge (4.2) in the solution, connect the electrodes to the potentiometer (4.1) and, after having verified the zero of the apparatus, note the value of the starting potential.
Titrate with the silver nitrate solution, by additions from the microburette (4.4) in increments of 0,1 ml. After each addition, await the stabilisation of the potential.
Continue the titration as specified in 5.1, starting from the fourth paragraph: ‘Record the volumes added and the corresponding values of the potential in the first two columns of a table …’.
Express the result of the analysis as the percentage of chlorine contained in the sample as received for analysis. Calculate the percentage of chlorine (Cl) content from the formula:
where:
T is the concentration of silver nitrate solution used, in mol/l
V4 is the result, in ml, of the blank test (5.2),
V5 is the value, in ml, of Veq corresponding to the determination (5.4),
m is the mass, in grams, of the test portion.
This document defines the procedure for the determination of copper content of straight ammonium nitrate fertilisers of high nitrogen content.
The sample is dissolved in dilute hydrochloric acid and the copper is determined by atomic absorption spectrophotometry.
Prepare this solution at the time of use.
Atomic absorption spectrophotometer with a copper lamp (324,8 nm).
Weigh, to the nearest 0,001 gram, 25 grams of the sample, place it in a 400-ml beaker, add carefully 20 ml of hydrochloric acid (3.1) (there may be a vigorous reaction due to carbon dioxide formation). Add more hydrochloric acid, if necessary. When effervescence has stopped, evaporate to dryness on a steam bath, stirring occasionally with a glass rod. Add 15 ml 6 mol/l hydrochloric acid solution (3.2) and 120 ml of water. Stir with the glass rod, which should be left in the beaker, and cover the beaker with a watch glass. Boil the solution gently until dissolution is complete and then cool.
Transfer the solution quantitatively into a 250-ml graduated flask, by washing the beaker with 5 ml 6 mol/l hydrochloric acid (3.2), and twice with 5 ml of boiling water, make up to the mark with 0,5 mol/l hydrochloric acid (3.3) and mix carefully.
Filter through a copper-free filter paper(3), discarding the first 50 ml.
Prepare a blank solution from which only the sample has been omitted and allow for this in the calculation of the final results.
Dilute the sample solution (5.1) and the blank test solution (5.2) with 0,5 mol/l hydrochloric acid solution (3.3) to a concentration of copper within the optimal measuring range of the spectrophotometer. Normally no dilution is needed.
By diluting the standard solution (3.6.1) with 0,5 mol/l hydrochloric acid solution (3.3), prepare at least five standard solutions corresponding to the optimal measuring range of the spectrophotometer (0 to 5,0 mg/l Cu). Before making up to the mark, add to every solution ammonium nitrate (3.4) to give concentration of 100 mg per ml.
Set up the spectrophotometer (4) at a wavelength of 324,8 nm. Use an oxidising air-acetylene flame. Spray successively, in triplicate, the calibration solution (5.3.2), the sample solution and the blank solution (5.3.1), washing the instrument through with distilled water between each spraying. Plot the calibration curve using the mean absorbances of every standard used as the ordinates and the corresponding concentrations of copper in μg/ml as the abscissae.
Determine the concentration of copper in the final sample and blank solutions by reference to the calibration curve.
Calculate the copper content of the sample taking into account the mass of the test sample, the dilutions carried out in the course of the analysis and the value of the blank. Express the result as mg Cu/kg.
This document defines the procedure for the determination or resistance to detonation of ammonium nitrate fertilisers of high nitrogen content.
The test sample is confined in a steel tube and subjected to detonation shock from an explosive booster charge. Propagation of the detonation is determined from the degree of crushing of lead cylinders on which the tube rests horizontally during the test.
:
1 500 to 1 600 kg/m3
:
7 300 to 7 700 m/s
:
500 (± 1) gram.
:
11 to 13 g/m
:
400 (± 2) mm.
:
hexogen/wax 95/5 or tetryl or similar secondary explosive, with or without added graphite.
:
1 500 to 1 600 kg/m3
:
19 to 21 mm
:
19 to 23 mm
:
diameter 7 to 7,3 mm, depth 12 mm.
:
113,1 to 115,0 mm
:
5,0 to 6,5 mm
:
1 005 (± 2) mm.
:
steel of good weldable quality
:
160 × 160 mm
:
5 to 6 mm
:
50 (± 1) mm
:
100 to 101 mm
:
soft lead, at least 99,5 % purity.
:
at least 1 000 mm
:
at least 150 mm
:
at least 150 mm
:
at least 300 kg if there is no firm base for the steel block.
:
1,5 to 2,5 mm
:
92 to 96 mm
:
64 to 67 mm
:
92 to 96 mm. Diameter to be matched to the internal diameter of the plastic or cardboard cylinder (4.3.8)
:
20 mm
There are two methods of initiation of the explosive in the booster charge, depending on the availability of equipment.
The booster charge prepared for use is shown in Figure 1.
The booster charge prepared for use is shown in Figure 2.
Taking the necessary safety precautions, place 10 grams of a secondary explosive (4.3.3) in a mould with an inside diameter of 19 to 21 mm and compress to the correct shape and density.
(The ratio of diameter: height should be roughly 1:1).
In the centre of the bottom of the mould there is a peg, 12 mm in height and 7,0 to 7,3 mm in diameter (depending on the diameter of the detonator used), which forms a cylindrical recess in the compressed cartridge for subsequent insertion of the detonator.
Place the explosive (4.3.1) into the cylinder (4.3.8) standing upright on a level surface, then press it down with a wooden die to give the explosive a cylindrical shape with a central recess. Insert the compressed pellet into this recess. Cover the cylindrically shaped explosive containing the compressed pellet with a wooden disc (4.3.10) having a central hole 7,0 to 7,3 mm in diameter for insertion of a detonator. Fix the wooden disc and the cylinder together with a cross of adhesive tape. Ensure that the hole drilled in the disc and the recess in the compressed pellet are coaxial by inserting the wooden rod (4.3.11).
At one end of the steel tube (4.3.4), drill two diametrically opposed holes 4 mm in diameter perpendicularly through the side wall at a distance of 4 mm from the edge.
Butt weld the bottom plate (4.3.5) to the opposite end of the tube, completely filling the right angle between the bottom place and the wall of the tube with weld metal around the entire circumference of the tube.
See Figures 1 and 2.
Repeat this charging method with another portion of the test sample. Finally, a further addition shall be made such that, after compaction by raising and dropping the tube 10 times and a total of 20 intermittent hammer blows, the charge fills the tube to a distance of 70 mm from its orifice.
The filling height of the sample must be adjusted in the steel tube so that the booster charge (4.4.1.1 or 4.4.1.2) to be inserted later will be in close contact with the sample over its entire surface.
Note: Make sure that the tube is in contact with all six lead cylinders; a slight curvature of the tube surface can be compensated for by rotating the tube about its longitudinal axis; if any of the lead cylinders is too tall, tap the cylinder in question carefully with a hammer until it is the required height.U.K.
Note: Should such firing sites not be available, the work can, if necessary, be done in a concrete-lined pit covered over with wooden beams. Detonation can cause steel fragments to be projected with high kinetic energy, therefore, firing must be carried out at a suitable distance from dwellings or thoroughfares.U.K.
Record for each of the marked lead cylinders, the degree of crushing expressed as a percentage of the original height of 100 mm. If the cylinders are crushed obliquely, record the highest and the lowest values and calculate the average.
Values for the following parameters are to be given in the test report for each of the detonation tests:
the values actually measures for the outside diameter of the steel tube and for the wall thickness,
the Brinell hardness of the steel tube,
the temperature of the tube and the sample shortly before firing,
the packing density (kg/m3) of the sample in the steel tube,
the height of each lead cylinder after firing, specifying the corresponding cylinder number,
method of initiation employed for the booster charge.
If, in each firing, the crushing of at least one lead cylinder is less than 5 %, the test shall be considered conclusive and the sample in conformity with the requirements of Annex III.2.
Figure 1
Figure 2
Figure 3
Textual Amendments
F1Words in Annex 3 para. 1.6 substituted (31.12.2020) by The Fertilisers and Ammonium Nitrate Material (Amendment) (EU Exit) Regulations 2019 (S.I. 2019/601), regs. 1(2), 5(22); 2020 c. 1, Sch. 5 para. 1(1)
A reaction time of one and a half hours, is sufficient in the case of most of the organic substances in the presence of silver nitrate catalyst.
Commercially available standard copper solution may be used.
Whatman 541 or equivalent.
The diameter of the disc must always correspond to the inside diameter of the cylinder.
NB: When the six peripheral lengths of cord are taut after assembly, the central cord must remain slightly slack.U.K.
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Mae’r llinell amser yma yn dangos y fersiynau gwahanol a gymerwyd o EUR-Lex yn ogystal ag unrhyw fersiynau dilynol a grëwyd ar ôl y diwrnod ymadael o ganlyniad i newidiadau a wnaed gan ddeddfwriaeth y Deyrnas Unedig.
Cymerir dyddiadau fersiynau’r UE o ddyddiadau’r dogfennau ar EUR-Lex ac efallai na fyddant yn cyfateb â’r adeg pan ddaeth y newidiadau i rym ar gyfer y ddogfen.
Ar gyfer unrhyw fersiynau a grëwyd ar ôl y diwrnod ymadael o ganlyniad i newidiadau a wnaed gan ddeddfwriaeth y Deyrnas Unedig, bydd y dyddiad yn cyd-fynd â’r dyddiad cynharaf y daeth y newid (e.e. ychwanegiad, diddymiad neu gyfnewidiad) a weithredwyd i rym. Am ragor o wybodaeth gweler ein canllaw i ddeddfwriaeth ddiwygiedig ar Ddeall Deddfwriaeth.
Defnyddiwch y ddewislen hon i agor dogfennau hanfodol sy’n cyd-fynd â’r ddeddfwriaeth a gwybodaeth am yr eitem hon o ddeddfwriaeth. Gan ddibynnu ar yr eitem o ddeddfwriaeth sy’n cael ei gweld gall hyn gynnwys:
liciwch ‘Gweld Mwy’ neu ddewis ‘Rhagor o Adnoddau’ am wybodaeth ychwanegol gan gynnwys