"carbonated natural mineral water" means water to which has been added carbon dioxide of an origin other than the water table or deposit from which the water comes.

TABLE C - INLAND WATERWAYS

"natural mineral water fortified with gas from the spring" means water whose content of carbon dioxide from the water table or deposit after decanting, if any, and bottling is greater than that established at source;

"Natural mineral water" means microbiologically wholesome water, within the meaning of Article 5, originating in an underground water table or deposit and emerging from a spring tapped at one or more natural or bore exits.

the protection of water tables and the purification of mine drainage water;

They fall into three categories to which the following descriptions respectively shall apply: (a) "naturally carbonated natural mineral water" means water whose content of carbon dioxide from the spring after decanting, if any, and bottling is the same as at source, taking into account where appropriate the reintroduction of a quantity of carbon dioxide from the same water table or deposit equivalent to that released in the course of those operations and subject to the usual technical tolerances;

Correct ρt using the table of densities ρt for water-alcohol mixtures (Table II of Annex II to this Chapter).

Water meters are divided, according to the values of Qmin and Qt defined above, into the three metrological classes in the following table:

The inclusion, following the specifications in Table 1d of AEWA/MOP2.9, of a further 48 species of waterbirds to Annex 2 of the Agreement and Table 1 of the Action Plan, and the inclusion of an additional 16 migratory populations of 12 species already listed in Annex 2 of the Agreement, to Table 1 of the Action Plan;

By way of derogation from Article 13 of Directive 91/271/EEC, the requirements for biodegradable industrial waste water shall not apply in Poland until 31 December 2010 in accordance with the table below:

Using the density ρ20, calculate the real alcoholic strength using the table giving the value of the alcoholic strength by volume (% vol.) at 20 °C as a function of the density at 20 °C of water-alcohol mixtures, i.e. the international table adopted by the International Legal Metrology Organisation in its Recommendation No 22.

The test mixture referred to in 6.1.9. of Annex I shall consist of the following (by volume): 92 75 % water (with a hardness of less than 205 g/tonne after evaporation), 5 % aqueous saturated salt (sodium chloride) solution and 2 75 % dust constituted in accordance with Tables I and II.

Storage in Centre region (FR, developing water table).

The third peculiarity stems from the area's autochthonous hydrography whereby the karstic water table is fed solely by a proportion of the rain that falls on it.

C orrect Ε„t to 20 using the table of densities Ε„T for water-alcohol mixtures (Table II of Annex II to th

C orrect ρt to 20 using the table of densities ρT for water-alcohol mixtures (Table II of Annex II to th e OIV's Manual of analysis methods (1994), pp.

Correc t ρt to 20 using the table of densities ρT for water-alcohol mixtures (Table II of Appendix II to the OIV's manual of analysis methods (1994), pp.

Common salt (including rock salt, sea salt and table salt); pure sodium chloride; salt liquors; sea water:

in the case of surface water in shallow lakes or virtually stagnant surface water, for parameters marked with an asterisk in the table in Annex II, this derogation being applicable only to lakes with a depth not exceeding 20 m, with an exchange of water slower than one year, and without a discharge of waste water into the water body.

Correc t Ε„t to 20 using the table of densities Ε„T for water-alcohol mixtures (Table II of Appendix II to the OIV's manual of analysis methods (1994), pp.

(a) the tables "Blue whiting in zone Vb (Community waters), VI, VII", "Blue whiting in zone VIIIabd" and "Sprat in zone IIIbcd (Community waters)" shall be replaced by the corresponding tables in Annex I to this Regulation;

For those chemicals which are poorly soluble in water, volatile or adsorbing, suitable methods are indicated in Table 1.

The table provides corrected values for surface-tension measurements taken after calibration with weights or calibration with water.

The approximate solubility is given in the table under that volume of added water in which complete dissolution of the sample occurs.

Salt (including table salt and denatured salt) and pure sodium chloride, whether or not in aqueous solution or containing added anti caking or free-flowing agents; sea water:

Salt (including table salt and denatured salt) and pure sodium chloride, whether or not in aqueous solution or containing added anti- caking or free- flowing agents; sea water:

The table giving the value of the alcoholic strength by volume (% vol) at 20 °C as a function of the density at 20 °C of water-alcohol mixtures is the international table adopted by the International Legal Metrology Organisation in its Recommendation No 22.

The table giving the value of the alcoholic strength by volume (% vol) at 20 °C as a function of the density at 20 °C of water-alcohol mixtures is the international table adopted by the International Legal Metrology Organisation in its Recommendation No 22.

where surface water undergoes natural enrichment in certain substances as a result of which it would exceed the limits laid down for categories Al, A2 and A3 in the table in Annex II;

toilet discharge system connections, trainset interior cleaning equipment (electrical sockets) and water filling adapters, as defined in Chapter 5 of this TSI, are indicated in Annex II, Tables II.1, II.2 and II.3 to this TSI.

By derogation from the table in Chapter 3.2 it is permitted to use a tank-container with tank-code L4BH instead of tank-code L4DH for the carriage of UN 3130, water-reactive liquid, toxic, III, n.o.s. under certain conditions.

To approximately 0,1 g of the sample (solid substances must be pulverized) in a glass-stoppered 10 ml graduated cylinder, increasing volumes of distilled water at room temperature are added according to the steps shown in the table below:

The numerical values and the list of parameters given in the table in Annex II, defining the physical, chemical and microbiological characteristics of surface water may be revised either at the request of a Member State or on a proposal from the Commission, whenever technical and scientific knowledge regarding methods of treatment is extended or drinking water standards are modified.

Whereas the requirements for discharges from urban waste water treatment plants to sensitive areas which are subject to eutrophication as drawn up in Table 2 of Annex I to Directive 91/271/EEC gave rise to problems of interpretation which it is vital to clarify;

For the purposes of this Directive surface water shall be divided according to limiting values into three categories, Al, A2 and A3, which correspond to the appropriate standard methods of treatment given in Annex I. These groups correspond to three different qualities of surface water, the respective physical, chemical and microbiological characteristics of which are set out in the table given in Annex II.

According to the variant chosen, place in the receiving flask an exactly measured quantity of standard sulphuric acid as indicated Table 1. Add the appropriate quantity of the chosen indicator solution (4.10.1 or 4.10.2) and finally, sufficient water to give a volume of 50 ml.

The reference values for alcoholic strength by volume (% vol) at 20 °C versus density at 20 °C for different water-alcohol mixtures that are to be used are those given in the international table adopted by the International Legal Metrology Organisation in its Recommendation No 22.

According to the variant chosen, place in the receiving flask a measured quantity of standard sulphuric acid as indicated in Table 1. Add the appropriate quantity of the chosen indicator solution (4.9.1 or 4.9.2) and, if necessary, water in order to obtain a volume of at least 50 ml.

According to the variant chosen, place in the receiving flask a measured quantity of standard sulphuric acid as indicated in Table 1. Add the appropriate quantity of the chosen indicator solution (4.9.1 or 4.9.2) and, if necessary, water in order to obtain a volume of at least 50 "ml.

The reference values for alcoholic strength by volume (% vol) at 20 °C versus density at 20 °C for different water-alcohol mixtures that are to be used are those given in the international table adopted by the International Legal Metrology Organisation in its Recommendation No 22.

However, because the concentration of cadmium in effluents depends on the volume of water involved, which differs for different processes and plants, the limit values, expressed in terms of the quantity of cadmium discharged in relation to the quantity of mercury handled, given in the above table, must be complied with in all cases.

Limit values expressed as concentrations which in principle must not be exceeded are given in the above table for the industrial sectors 2, 3, 4, 5 and 6. In no instance may limit values expressed as maximum concentrations be greater than those expressed as maximum quantities divided by water requirements per kilogram of cadmium handled.

However, because the concentration of mercury in effluents depends on the volume of water involved, which differs for different processes and plants, the limit values, expressed in terms of the quantity of mercury discharged in relation to the quantity of mercury handled or to the installed vinyl chloride production capacity, given in the above table, must be complied with in all cases.

Limit values expressed as concentrations which in principle must not be exceeded are given in the above table for the industrial sectors 1 to 4. In no instance may limit values expressed as maximum concentrations be greater than those expressed as maximum quantities divided by water requirements per kilogram of mercury handled or per tonne of installed vinyl chloride production capacity.

Nevertheless, as the concentration of mercury in effluents depends on the volume of water involved, and as this differs from one process and establishment to the next, the limit values, expressed in terms of the quantity of mercury discharged as compared with the quantity of mercury treated or the installed vinyl chloride capacity given in the above table, must be complied with at all times.