natgillin/translations-raw huggingface dataset:
The following guidelines should be met as far as practicable:
V največji možni meri je treba slediti naslednjim smernicam:
the flow around the inlet sampling probe should be unrestricted, without any obstructions affecting the airflow in the vicinity of the sampler (normally some metres away from buildings, balconies, trees and other obstacles and at least 0,5 m from the nearest building in the case of sampling points representing air quality at the building line);
pretok okrog vzorčevalne sonde na dovodu naj bo nemoten, tako da na pretok zraka v bližini vzorčevalnika ne bi vplivale kakršne koli prepreke (navadno nekaj metrov od zgradb, balkonov, dreves in drugih ovir ter vsaj 0,5 m od najbližje stavbe, če gre za vzorčevalna mesta, reprezentativna za kakovost zraka ob gradbeni liniji),
in general, the inlet sampling point should be between 1,5 m (the breathing zone) and 4 m above the ground.
na splošno naj bo vzorčevalno mesto na dovodu v višini 1,5 m (pas dihanja) do 4 m nad tlemi.
Higher positions (up to 8 m) may be necessary in some circumstances.
V nekaterih okoliščinah bi lahko bila potrebna višja postavitev (do 8 m).
Higher siting may also be appropriate if the station is representative of a large area;
Višja postavitev bi utegnila biti primerna tudi, če je postaja reprezentativna za večje področje,
the inlet probe should not be positioned in the immediate vicinity of sources in order to avoid direct intake of emissions unmixed with ambient air;
sonda na dovodu naj ne bo nameščena v neposredni bližini virov, da bi se izognili neposrednemu zajemu emisij, ki niso premešane z zunanjim zrakom,
the sampler’s exhaust outlet should be positioned so that recirculation of exhaust air to the sample inlet is avoided;
izpuh vzorčevalnika je treba namestiti tako, da ne pride do ponovnega zajema izpušnega zraka na dovodu v vzorčevalnik,
traffic-orientated sampling points should be at least 25 metres from the edge of major junctions and at least 4 m from the centre of the nearest traffic lane; inlets should be sited so as to be representative of air quality near the building line;
prometno usmerjena vzorčevalna mesta naj bodo najmanj 25 m od roba večjih križišč in najmanj 4 m od sredine najbližjega prometnega pasu; dovodi naj bodo postavljeni tako, da so reprezentativni za kakovost zraka ob gradbeni liniji,
for the deposition measurements in rural background areas, the EMEP guidelines and criteria should be applied as far as practicable and where not provided for in the Annexes.
za meritve usedanja v območjih s podeželskim ozadjem se uporabljajo smernice in merila EMEP, v kolikor je to praktično in če ni drugače predvideno v teh prilogah.
The following factors may also be taken into account:
Upoštevajo se lahko tudi naslednji dejavniki:
interfering sources
moteči viri,
security
varnost,
access
dostop,
availability of electrical power and telephone communications
razpoložljivost električne energije in telefonskih povezav,
visibility of the site in relation to its surroundings
vidnost lokacije glede na okolico,
safety of the public and operators
varnost javnosti in izvajalcev,
the desirability of co-locating sampling points for different pollutants
zaželenost sopostavitve vzorčevalnih mest za druga onesnaževala,
planning requirements.
zahteve prostorskega planiranja.
Documentation and review of site selection
Dokumentacija in pregled izbora lokacije
The site selection procedures should be fully documented at the classification stage by such means as compass-point photographs of the surrounding area and a detailed map.
V fazi razvrščanja naj bi se v celoti dokumentirali postopki izbora lokacije, na primer z orientacijskimi fotografijami bližnje okolice in podrobno karto.
Sites should be reviewed at regular intervals with repeated documentation to ensure that selection criteria remain valid over time.
Lokacije je treba pregledovati v rednih intervalih in jih ponovno dokumentirati, tako da bi izbirna merila zagotovo ostala veljavna.
Criteria for determining numbers of sampling points for fixed measurement of concentrations of arsenic, cadmium, nickel and benzo(a)pyrene in ambient air
Merila za določanje števila vzorčevalnih mest za merjenje koncentracij arzena, kadmija, niklja in benzo(a)pirena v zunanjem zraku
Minimum number of sampling points for fixed measurement to assess compliance with target values for the protection of human health in zones and agglomerations where fixed measurement is the sole source of information.
Najmanjše število vzorčevalnih mest na stalnem merilnem mestu za oceno skladnosti s ciljnimi vrednostmi za zaščito zdravja ljudi v območjih in strnjenih naseljih, kjer je meritev na stalnem merilnem mestu edini vir informacij.
Diffuse sources
Razpršeni viri
Population of agglomeration or zone
Prebivalstvo območja ali strnjenega naselja
(thousands)
(tisoč)
If maximum concentrations exceed the upper assessment threshold [1]
Če najvišje koncentracije presežejo zgornji ocenjevalni prag [1]
If maximum concentrations are between the upper and lower assessment thresholds
Če so najvišje koncentracije med zgornjim in spodnjim ocenjevalnim pragom
Point sources
Točkovni viri
For the assessment of pollution in the vicinity of point sources, the number of sampling points for fixed measurement should be determined taking into account emission densities, the likely distribution patterns of ambient air pollution and potential exposure of the population.
Za oceno onesnaženosti v bližini točkovnih virov, se število vzorčevalnih mest za meritve na stalnem merilnem mestu določi ob upoštevanju gostote emisije, verjetnih porazdelitvenih vzorcev onesnaženosti zunanjega zraka in možnosti izpostavljenosti prebivalstva.
The sampling points should be sited such that the application of BAT as defined by Article 2(11) of Directive 96/61/EC can be monitored.
Vzorčevalna mesta bi morala biti postavljena tako, da je mogoče spremljati uporabo BAT, kakor je opredeljeno v členu 2(11) Direktive 96/61/ES.
To include at least one urban-background station and for benzo(a)pyrene also one traffic-oriented station provided this does not increase the number of sampling points.
Vključi se najmanj ena postaja z urbano okolico, za benzo(a)piren pa tudi ena prometu izpostavljena postaja, pod pogojem, da to ne poveča števila vzorčevalnih mest.
Data quality objectives and requirements for air quality models
Cilji kakovosti podatkov in zahteve za modele kakovosti zraka
I. Data quality objectives
I. Cilji kakovosti podatkov
The following data quality objectives are provided as a guide to quality assurance.
Za zagotavljanje kakovosti so kot vodilo predvideni naslednji cilji kakovosti podatkov.
Arsenic, cadmium and nickel
Arzen, kadmij in nikelj
Polycyclic aromatic hydrocarbons other than benzo(a)pyrene, total gaseous mercury
Policiklični aromatski ogljikovodiki, razen benzo(a)piren, celotno plinasto živo srebro
Total deposition
Celotno usedanje
Uncertainty
Negotovost
Fixed and indicative measurements
Meritve na stalnem merilnem mestu in indikativne meritve
Minimum data capture
Najmanjše zajetje podatkov
Minimum time coverage:
Najmanjši časovni interval:
Fixed measurements
Meritve na stalnem merilnem mestu
Indicative measurements [1]
Indikativne meritve [1]
The uncertainty (expressed at a 95 % confidence level) of the methods used for the assessment of ambient air concentrations will be evaluated in accordance with the principles of the CEN Guide to the expression of uncertainty in measurement (ENV 13005-1999), the methodology of ISO 5725:1994, and the guidance provided in the CEN Report, ‘Air quality — Approach to uncertainty estimation for ambient air reference measurement methods’ (CR 14377:2002E).
Negotovost (izražena s 95 % stopnjo zaupanja) metod uporabljenih za oceno koncentracij zunanjega zraka bo ocenjena v skladu z načeli Navodil CEN za izražanje negotovosti meril (ENV 13005-1999), metodologijo ISO 5725:1994 in navodili iz Poročila CEN o kakovosti zraka — Pristop k oceni negotovosti referenčnih meritev zunanjega zraka (CR 14377:2002E).
The percentages for uncertainty are given for individual measurements, which are averaged over typical sampling times, for a 95 % confidence interval.
Odstotki negotovosti so podani za individualne meritve, na osnovi povprečja tipičnih merilnih časov za obdobje zaupanja 95 %.
The uncertainty of the measurements should be interpreted as being applicable in the region of the appropriate target value.
Negotovost meritve se razume kot da je uporabna na območju ustrezne ciljne vrednosti.
Fixed and indicative measurements must be evenly distributed over the year in order to avoid skewing of results.
Meritve na stalnem mestu in indikativne meritve morajo biti enakomerno razporejene čez leto v izogib asimetiriji rezultatov.
The requirements for minimum data capture and time coverage do not include losses of data due to regular calibration or normal maintenance of the instrumentation.
Zahteve glede najmanjšega zajetja podatkov in najmanjšega časovnega intervala ne vključujejo izgube podatkov zaradi rednega umerjanja ali rednega vzdrževanja instrumentacije.
Twenty-four-hour sampling is required for the measurement of benzo(a)pyrene and other polycyclic aromatic hydrocarbons.
Za meritve benzo(a)pirena in drugih policikličnih aromatskih ogljikovodikov se zahteva štiriindvajseturno vzorčenje.
With care, individual samples taken over a period of up to one month can be combined and analysed as a composite sample, provided the method ensures that the samples are stable for that period.
Posamezne vzorce iz največ enomesečnega obdobja se lahko s previdnostjo kombinira in analizira kot sestavljen vzorec pod pogojem, da metoda zagotavlja stabilnost vzorcev za to obdobje.
The three congeners benzo(b)fluoranthene, benzo(j)fluoranthene, benzo(k)fluoranthene can be difficult to resolve analytically.
Tri sorodne snovi benzo(b)fluoranten, benzo(j)fluoranten in benzo(k)fluoranten so lahko analitično težko določljive.
In such cases they can be reported as sum.
V takšnih primerih so lahko predstavljene kot vsota.
Twenty-four hour sampling is also advisable for the measurement of arsenic, cadmium and nickel concentrations.
Štiriindvajset urno vzorčenje je priporočljivo tudi za meritve koncentracije arzena, kadmija in niklja.
Sampling must be spread evenly over the weekdays and the year.
Vzorčenje mora biti enakomerno porazdeljeno po tednu in letu.
For the measurement of deposition rates monthly, or weekly, samples throughout the year are recommended.
Za meritve stopenj usedanja mesečno ali tedensko so priporočeni vzorci skozi vse leto.
Member States may use wet only instead of bulk sampling if they can demonstrate that the difference between them is within 10 %.
Države članice lahko uporabijo mokro vzorčenje samo namesto masivnega vzorčenja, če lahko dokažejo, da se razlikujeta do 10 %.
Deposition rates should generally be given as μg/m2 per day.
Stopnje usedanja se običajno izražajo v μg/m2 na dan.
Member States may apply a minimum time coverage lower than indicated in the table, but not lower than 14 % for fixed measurements and 6 % for indicative measurements provided that they can demonstrate that the 95 % expanded uncertainty for the annual mean, calculated from the data quality objectives in the table according to ISO 11222:2002 — ‘Determination of the uncertainty of the time average of air quality measurements’ will be met.
Države članice lahko uporabijo nižjo minimalno časovno pokritost, kakor je prikazana v preglednici, vendar ne nižjo od 14 % za meritve na stalnem mestu in 6 % za indikativne meritve pod pogojem, da lahko dokažejo, da bo izpolnjena 95 % razširjena negotovost za letno povprečje, izračunana iz ciljev glede kakovosti podatkov v preglednici ISO 11222:2002 — „Določitev negotovosti povprečnega časa za meritve kakovosti zraka“.
Requirements for air quality models
Zahteve za modele kakovosti zraka
Where an air quality model is used for assessment, references to descriptions of the model and information on the uncertainty shall be compiled.
Kadar se za ocenjevanje uporablja model kakovosti zraka, se pripravi opis modela ter podatki o zanesljivosti.
The uncertainty for modelling is defined as the maximum deviation of the measured and calculated concentration levels, over a full year, without taking into account the timing of the events.
Negotovost modeliranja se določi kot največji odklon izmerjenih in izračunanih koncentracij v celotnem letu, ne da bi se upoštevala časovna razporeditev dogodkov.
Requirements for objective estimation techniques
Zahteve za objektivne metode ocenjevanja
Where objective estimation techniques are used, the uncertainty shall not exceed 100 %.
Če se uporabljajo objektivne metode ocenjevanja, negotovost ne sme presegati 100 %.
Standardisation
Standardizacija
For substances to be analysed in the PM10 fraction, the sampling volume refers to ambient conditions.
Za snovi, ki se analizirajo v frakciji PM10 se količina vzorcev nanaša na zunanje pogoje.
Indicative measurement being measurements which are performed at reduced regularity but fulfil the other data quality objectives.
Indikativne meritve so meritve, ki se izvajajo z zmanjšano rednostjo vendar izpolnjujejo druge cilje glede kakovosti podatkov.
Reference methods for assessment of concentrations in ambient air and deposition rates
Referenčne metode za ocenjevanje koncentracij v zunanjem zraku ter stopenj usedanja
I. Reference method for the sampling and analysis of arsenic, cadmium and nickel in ambient air
I. Referenčna metoda za vzorčenje in analizo arzena, kadmija in niklja v zunanjem zraku
The reference method for the measurement of arsenic, cadmium and nickel concentrations in ambient air is currently being standardised by CEN and shall be based on manual PM10 sampling equivalent to EN 12341, followed by digestion of the samples and analysis by Atomic Absorption Spectrometry or ICP Mass Spectrometry.
Referenčna metoda za merjenje koncentracij arzena, kadmija in niklja v zunanjem zraku je trenutno v postopku standardizacije pri CEN in bo temeljila na ročnem vzorčenju PM10, enakovrednem EN 12341, ki mu bo sledil razklop vzorcev in analiza z atomsko absorpcijsko spektrometrijo (AAS) ali induktivno sklopljeno plazmo z masno spektrometrijo ICP.
In the absence of a CEN standard method, Member States are allowed to use national standard methods or ISO standard methods.
Če standardne metode CEN ni, smejo države članice uporabljati nacionalne standardne metode ali standardne metode ISO.
A Member State may also use any other methods which it can demonstrate give results equivalent to the above method.
Država članica lahko uporabi tudi druge metode, za katere lahko dokaže, da dajejo enakovredne rezultate kot zgornja metoda.
Reference method for the sampling and analysis of polycyclic aromatic hydrocarbons in ambient air
Referenčna metoda za vzorčenje in analizo policikličnih aromatskih ogljikovodikov v zunanjem zraku
The reference method for the measurement of benzo(a)pyrene concentrations in ambient air is currently being standardised by CEN and shall be based on manual PM10 sampling equivalent to EN 12341.
Referenčna metoda za merjenje benzo(a)pirena v zunanjem zraku je trenutno v postopku standardizacije pri CEN in bo temeljila na ročnem vzorčenju PM10, enakovrednem EN 12341.
In the absence of a CEN standard method, for benzo(a)pyrene or the other polycyclic aromatic hydrocarbons referred to in Article 4(8), Member States are allowed to use national standard methods or ISO methods such as ISO standard 12884.
Če standardne metode CEN ni, smejo države članice za benzo(a)piren in druge policiklične aromatske ogljikovodike iz člena 4(8) uporabljati nacionalne standardne metode ali metode ISO, kakor je denimo ISO standard 12884.
Reference method for the sampling and analysis of mercury in ambient air
Referenčna metoda za vzorčenje in analizo policikličnih aromatskih ogljikovodikov v zunanjem zraku
The reference method for the measurement of total gaseous mercury concentrations in ambient air shall be an automated method based on Atomic Absorption Spectrometry or Atomic Fluorescence Spectrometry.
Referenčna metoda za merjenje skupnega plinastega živega srebra je avtomatizirana metoda, ki temelji na atomski absorpcijski spektrometriji ali atomski fluorescenčni spektrometriji.
In the absence of a CEN standardised method, Member States are allowed to use national standard methods or ISO standard methods.
Če standardizirane metode CEN ni, smejo države članice uporabljati nacionalne standardne metode ali standardne metode ISO.
Reference method for the sampling and analysis of the deposition of arsenic, cadmium, mercury, nickel and polycyclic aromatic hydrocarbons
Referenčna metoda za vzorčenje in analizo usedanja arzena, kadmija, živega srebra, niklja in policikličnih aromatskih ogljikovodikov
The reference method for the sampling of deposited arsenic, cadmium, mercury, nickel and polycyclic aromatic hydrocarbons shall be based on the exposition of cylindrical deposit gauges with standardised dimensions.
Referenčna metoda za vzorčenje usedlin arzena, kadmija, živega srebra, niklja in policikličnih aromatskih ogljikovodikov temelji na ekspoziciji cilindričnih naprav za nadzor usedanja standardiziranih dimenzij.
In the absence of a CEN standardised method, Member States are allowed to use national standard methods.
Če standardizirane metode CEN ni, smejo države članice uporabljati nacionalne standardne metode.
V. Reference air quality modelling techniques
V. Referenčno modeliranje kakovosti zraka
Reference air quality modelling techniques cannot be specified at present.
V tem trenutku ni mogoče določiti referenčnega modeliranja kakovosti zraka.
Any amendments to adapt this point to scientific and technical progress must be adopted in accordance with the procedure laid down in Article 6.
Vse spremembe te točke, da se jo prilagodi znanstvenemu in tehnološkemu napredku, morajo biti sprejete v skladu s postopkom iz člena 6.
The upper and lower assessment thresholds for arsenic, cadmium, nickel and benzo(a)pyrene in ambient air shall be those laid down in Section I of Annex II.
Zgornji in spodnji ocenjevalni prag za arzen, kadmij, nikelj in benz(o)piren v zunanjem zraku sta določena v oddelku I Priloge II.
The classification of each zone or agglomeration for the purposes of this Article shall be reviewed at least every five years in accordance with the procedure laid down in Section II of Annex II.
Razvrstitev vsakega območja ali strnjenega naselja za namen tega člena se preveri vsakih pet let v skladu s postopkom iz oddelka II Priloge II.
Data quality objectives are laid down in Section I of Annex IV.
Cilji kakovosti podatkov so določeni v oddelku I Priloge IV.
Where air quality models are used for assessment, Section II of Annex IV shall apply.
Kadar se za ocenjevanje uporabljajo modeli kakovosti zraka, se uporablja oddelek II Priloge IV.
Directive 2004/108/EC of the European Parliament and of the Council
Direktiva 2004/108/ES Evropskega parlamenta in Sveta
on the approximation of the laws of the Member States relating to electromagnetic compatibility and repealing Directive 89/336/EEC
o približevanju zakonodaj držav članic v zvezi z elektromagnetno združljivostjo in razveljavitvi Direktive 89/336/EGS
Having regard to the Treaty establishing the European Community, and in particular Article 95 thereof,
ob upoštevanju Pogodbe o ustanovitvi Evropske skupnosti in zlasti člena 95 Pogodbe,
Acting in accordance with the procedure referred to in Article 251 of the Treaty [2],
v skladu s postopkom, določenim v členu 251 Pogodbe [2],
Council Directive 89/336/EEC of 3 May 1989 on the approximation of laws of the Member States relating to electromagnetic compatibility [3] has been the subject of a review under the initiative known as Simpler Legislation for the Internal Market (SLIM).
Direktiva Sveta 89/336/EGS z dne 3. maja 1989 o približevanju zakonodaj držav članic v zvezi z elektromagnetno združljivostjo [3] je bila pregledana na podlagi pobude za enostavnejšo zakonodajo za notranji trg (SLIM).
Both the SLIM process and a subsequent in-depth consultation have revealed the need to complete, reinforce and clarify the framework established by Directive 89/336/EEC.
Tako postopek SLIM kot tudi kasnejša podrobnejša posvetovanja so pokazala potrebo po dopolnitvi, okrepitvi in razjasnitvi okvirja, ki ga določa Direktiva 89/336/EGS.
Member States are responsible for ensuring that radiocommunications, including radio broadcast reception and the amateur radio service operating in accordance with International Telecommunication Union (ITU) radio regulations, electrical supply networks and telecommunications networks, as well as equipment connected thereto, are protected against electromagnetic disturbance.
Države članice so odgovorne za zaščito radiokomunikacij, vključno s sprejemanjem radiodifuznih in radioamaterskih storitev, ki delujejo v skladu s pravilnikom o radiokomunikacijah Mednarodne telekomunikacijske zveze (ITU), omrežij za dobavo električne energije in telekomunikacij kot tudi s tem povezane opreme pred elektromagnetnimi motnjami.
Provisions of national law ensuring protection against electromagnetic disturbance should be harmonised in order to guarantee the free movement of electrical and electronic apparatus without lowering justified levels of protection in the Member States.
Določbe nacionalne zakonodaje, ki zagotavljajo zaščito pred elektromagnetnimi motnjami, morajo biti usklajene, da se zagotovi prost pretok električnih in elektronskih aparatov, ne da bi znižali upravičene ravni zaščite v državah članicah.
Protection against electromagnetic disturbance requires obligations to be imposed on the various economic operators.
Za zaščito pred elektromagnetnimi motnjami je treba naložiti obveznosti različnim gospodarskim subjektom.
Those obligations should be applied in a fair and effective way in order to achieve such protection.
Da bi se zagotovilo zaščito je treba te obveznosti izvajati na pravičen in učinkovit način.
The electromagnetic compatibility of equipment should be regulated with a view to ensuring the functioning of the internal market, that is to say, of an area without internal frontiers in which the free movement of goods, persons, services and capital is assured.
Elektromagnetno združljivost opreme je treba urediti tako, da se zagotovi delovanje notranjega trga, tj. območja brez notranjih meja, na katerem je zagotovljen prost pretok blaga, oseb, storitev in kapitala.
The equipment covered by this Directive should include both apparatus and fixed installations.
V opremo, ki jo zajema ta direktiva, je treba vključiti aparate in nepremične naprave.
However, separate provision should be made for each.
Vendar pa so za obe vrsti opreme potrebne ločene določbe.
This is so because, whereas apparatus as such may move freely within the Community, fixed installations on the other hand are installed for permanent use at a predefined location, as assemblies of various types of apparatus and, where appropriate, other devices.
Za aparate kot take velja namreč prost pretok znotraj Skupnosti, medtem ko so nepremične naprave vgrajene za stalno uporabo na določenem mestu v sklope raznih vrst aparatov in, če je to primerno, drugih naprav.
The composition and function of such installations correspond in most cases to the particular needs of their operators.
Sestava in delovanje takih nepremičnih naprav največkrat odgovarja posebnim potrebam subjektov, ki z njimi upravljajo.
Radio equipment and telecommunications terminal equipment should not be covered by this Directive since they are already regulated by Directive 1999/5/EC of the European Parliament and of the Council of 9 March 1999 on radio equipment and telecommunications terminal equipment and the mutual recognition of their conformity [4].
Ta direktiva naj ne zajema radijske telekomunikacijske terminalske opreme, ker slednjo ureja že Direktiva 1999/5/ES Evropskega Parlamenta in Sveta z dne 9. marca 1999 o radijski opremi in telekomunikacijski terminalski opremi ter medsebojnem priznavanju skladnosti te opreme [4].
The electromagnetic compatibility requirements in both Directives achieve the same level of protection.
Zahteve glede elektromagnetne združljivosti obeh direktiv dosegajo isto raven zaščite.