natgillin/translations-raw huggingface dataset:
make a best-possible estimation of all relevant processes involved taking into account realistic parameters and assumptions,
zagotavljajo najboljšo možno oceno vseh relevantnih postopkov, pri čemer se upoštevajo realistični parametri in predpostavke,
where possible be reliably validated with measurements carried out under circumstances relevant for the use of the model,
kadar je to mogoče, so zanesljivo preverjeni z meritvami, izvedenimi v pogojih, ki ustrezajo uporabi modela,
The information provided shall, where relevant, include that referred to in Section 7 of Part A of the Annex to Regulation (EU) No 283/2013.
Kadar je ustrezno, predložene informacije vključujejo informacije iz oddelka 7 dela A Priloge k Uredbi (EU) št. 283/2013.
For solid plant protection products, treated and coated seeds there shall be an assessment of the risk from dust drift on to non-target species during application or sowing.
Za trdna fitofarmacevtska sredstva, tretirana in obložena semena se izvede ocena tveganja zaradi zanašanja prahu na neciljne vrste med nanašanjem ali sejanjem.
Until agreed dust dissipation rates are available, then likely exposure levels shall be determined using a range of application techniques, suitable dust measurement methodology and, where appropriate, mitigation measures.
Dokler niso na voljo sprejete stopnje razpada prahu, se možne stopnje izpostavljenosti določijo z različnimi tehnikami nanašanja, primerno metodologijo za merjenje prahu in, kadar je primerno, ukrepi za ublažitev.
Laboratory studies on soil degradation shall provide best possible estimates of the time required for degradation of 50 % and 90 % (DegT50lab and DegT90lab) of the active substance under laboratory conditions.
Z laboratorijskimi študijami o razgradnji v tleh se zagotovi najboljša možna ocena časa za 50- in 90-odstotno razgradnjo (DegT50lab in DegT90lab) aktivne snovi v laboratorijskih pogojih.
The persistence and behaviour of plant protection products in soil shall be investigated unless it is possible to extrapolate from data obtained on the active substance and metabolites, breakdown and reaction products in accordance with the requirements set out in point 7.1.2.1 of Part A of the Annex to Regulation (EU) No 283/2013.
Obstojnost in obnašanje fitofarmacevtskih sredstev v tleh se preučita le, kadar podatkov ni mogoče ekstrapolirati iz podatkov o aktivni snovi in metabolitih ter razgradnih in reakcijskih produktih, pridobljenih v skladu z zahtevami iz točke 7.1.2.1 dela A Priloge k Uredbi (EU) št. 283/2013.
Where it is not possible to extrapolate from anaerobic incubation data obtained on the active substance and metabolites, breakdown and reaction products in accordance with the requirements set out in point 7.1.2.1 of Part A of the Annex to Regulation (EU) No 283/2013, an anaerobic degradation study shall be submitted unless the applicant shows that exposure of the plant protection product containing the active substance to anaerobic conditions is unlikely to occur for the intended uses.
Kadar ekstrapolacija iz podatkov o anaerobni inkubaciji za aktivno snov in metabolite ter razgradne in reakcijske produkte, pridobljenih v skladu z zahtevami iz točke 7.1.2.1 dela A Priloge k Uredbi (EU) št. 283/2013, ni možna, se predloži študija o anaerobni razgradnji, razen če vlagatelj dokaže, da izpostavljenost fitofarmacevtskega sredstva, ki vsebuje zadevno aktivno snov, anaerobnim pogojem pri predvidenih načinih uporabe ni verjetna.
Studies on the rate of aerobic degradation of the active substance shall be reported for at least four soils.
Študije o stopnji aerobne razgradnje aktivne snovi se navedejo za najmanj štiri vrste tal.
Soil properties shall be comparable to those used for the aerobic studies performed in accordance with point 7.1.1 and 7.1.2.1 of Part A of the Annex to Regulation (EU) No 283/2013.
Lastnosti tal so primerljive z lastnostmi tal, ki se uporabljajo za aerobne študije, izvedene v skladu s točkama 7.1.1 in 7.1.2.1 dela A Priloge k Uredbi (EU) št. 283/2013.
Studies on the rate of anaerobic degradation of the active substance shall be carried out using the same procedure and comparable soil as for the anaerobic study performed in accordance with point 7.1.1.2 of Part A of the Annex to Regulation (EU) No 283/2013.
Študije o stopnji anaerobne razgradnje aktivne snovi se izvedejo po enakem postopku in s primerljivo vrsto tal, kot se uporabljata za anaerobno študijo, izvedeno v skladu s točko 7.1.1.2 dela A Priloge k Uredbi (EU) št. 283/2013.
The kinetic formation fraction and degradation rates of potentially relevant metabolites shall be established, in the studies under both aerobic and anaerobic conditions by extension of the study for the active substance, where it is not possible to extrapolate from points 7.1.2.1.2 and 7.1.2.1.4 of Part A of the Annex to Regulation (EU) No 283/2013.
S študijami v aerobnih in anaerobnih pogojih se določijo kinetično nastali deli in stopnje razgradnje potencialno relevantnih metabolitov, pri čemer se razširi študija za aktivno snov, kadar ni možna ekstrapolacija iz točk 7.1.2.1.2 in 7.1.2.1.4 dela A Priloge k Uredbi (EU) št. 283/2013.
In order to assess the influence of temperature on degradation, a calculation with an adequate Q10 factor or an adequate number of additional studies at a range of temperatures shall be performed.
Za oceno vpliva temperature na razgradnjo se izvede izračun z ustreznim faktorjem Q10 ali ustrezno število dodatnih študij pri različnih temperaturah.
Reliable DegT50 and 90 values for metabolites, breakdown and reaction products shall be provided for at least three soils from the studies under aerobic conditions.
Za vsaj tri vrste tal iz študij v aerobnih pogojih se zagotovijo zanesljive vrednosti DegT50 in 90 za metabolite, razgradne in reakcijske produkte.
The soil dissipation studies shall provide best-possible estimates of the time taken for dissipation of 50 % and 90 % (DisT50field and DisT90field) and if possible the time taken for degradation of 50 % and 90 % (DegT50field and DegT90field), of the active substance under field conditions.
S študijami o razpadu v tleh se zagotovi čim boljša ocena časa, ki je potreben za 50- in 90-odstoten razpad (DisT50teren in DisT90teren) aktivne snovi, ter, kadar je mogoče, časa, ki je potreben za 50- in 90-odstotno razgradnjo (DegT50teren in DegT90teren) aktivne snovi v terenskih pogojih.
Where relevant, information on metabolites, breakdown and reaction products shall be reported.
Kadar je ustrezno, se navedejo informacije o metabolitih ter razgradnih in reakcijskih produktih.
The dissipation and behaviour of plant protection products in soil shall be investigated unless it is possible to extrapolate from data obtained on the active substance and metabolites, breakdown and reaction products in accordance with the requirements set out in point 7.1.2.2.1 of Part A of the Annex to Regulation (EU) No 283/2013.
Razpad in obnašanje fitofarmacevtskih sredstev v tleh se preučita le, kadar podatkov ni mogoče ekstrapolirati iz podatkov o aktivni snovi in metabolitih ter razgradnih in reakcijskih produktih, pridobljenih v skladu z zahtevami iz točke 7.1.2.2.1 dela A Priloge k Uredbi (EU) št. 283/2013.
Individual studies on a range of representative soils (normally at least four different types at different geographical locations) shall be continued until at least 90% of the amount applied has dissipated from the soil or been transformed to substances that are not the subject of the investigation.
Posamezne študije z različnimi reprezentativnimi vrstami tal (običajno z vsaj štirimi različnimi vrstami tal na različnih geografskih lokacijah) se izvajajo, dokler vsaj 90 % nanesene količine ne razpade v tleh ali se pretvori v snovi, ki jih ta preučitev ne zadeva.
The tests shall provide sufficient data to evaluate the possibility of accumulation of residues of the active substance and of metabolites, breakdown and reaction products.
S preskusi se zagotovi dovolj podatkov za oceno možnega kopičenja ostankov aktivne snovi in metabolitov ter razgradnih in reakcijskih produktov.
Soil accumulation studies shall be reported unless it is possible to extrapolate from data obtained on the active substance and metabolites, breakdown and reaction products in accordance with the requirements set out in point 7.1.2.2.2 of Part A of the Annex to Regulation (EU) No 283/2013.
Študije o kopičenju v tleh se navedejo le, kadar podatkov ni mogoče ekstrapolirati iz podatkov o aktivni snovi in metabolitih ter razgradnih in reakcijskih produktih, pridobljenih v skladu z zahtevami iz točke 7.1.2.2.2 dela A Priloge k Uredbi (EU) št. 283/2013.
Long term field studies shall be performed on at least two relevant soils at different geographical locations and involve multiple applications.
Dolgoročne terenske študije se izvedejo na vsaj dveh relevantnih vrstah tal na različnih geografskih lokacijah in z večkratnimi nanosi.
The information made available shall provide sufficient data to evaluate the mobility and leaching potential of the active substance and metabolites, breakdown and reaction products.
Z razpoložljivimi informacijami se zagotovi dovolj podatkov za oceno mobilnosti in možnosti izpiranja aktivne snovi in metabolitov ter razgradnih in reakcijskih produktov.
The mobility of plant protection products in soil shall be investigated unless it is possible to extrapolate from data obtained in accordance with the requirements set out in points 7.1.2 and 7.1.3.1 of Part A of the Annex to Regulation (EU) No 283/2013.
Mobilnost fitofarmacevtskih sredstev v tleh se preuči le, kadar podatkov ni mogoče ekstrapolirati iz podatkov, pridobljenih v skladu z zahtevami iz točk 7.1.2 in 7.1.3.1 dela A Priloge k Uredbi (EU) št. 283/2013.
The same provisions as provided under points 7.1.2 and 7.1.3.1 of Part A of the Annex to Regulation (EU) No 283/2013 apply.
Uporabljajo se določbe iz točk 7.1.2 in 7.1.3.1 dela A Priloge k Uredbi (EU) št. 283/2013.
the mobility in soil,
mobilnosti v tleh;
the potential for leaching to ground water,
možnosti izpiranja v podtalnico;
The decision whether lysimeter studies are to be carried out, as an experimental outdoor study in the framework of a tiered leaching assessment scheme shall take into account the results of degradation and mobility studies and the calculated PECGW.
Pri odločanju o izvedbi študij z lizimetrom, pri čemer se izvedejo kot eksperimentalna študija na prostem v okviru večstopenjskega sistema ocenjevanja izpiranja, se upoštevajo rezultati študij o razgradnji in mobilnosti ter izračunani PECGW.
The type of study to be conducted shall be discussed with the national competent authorities.
Vrsta študije, ki jo je treba izvesti, se preuči skupaj z nacionalnimi pristojnimi organi.
These studies shall be performed unless it is possible to extrapolate from data obtained on the active substance and metabolites, breakdown and reaction products in accordance with the requirements set out in point 7.1.4.2 of Part A of the Annex to Regulation (EU) No 283/2013.
Te študije se izvedejo le, kadar podatkov ni mogoče ekstrapolirati iz podatkov o aktivni snovi in metabolitih ter razgradnih in reakcijskih produktih, pridobljenih v skladu z zahtevami iz točke 7.1.4.2 dela A Priloge k Uredbi (EU) št. 283/2013.
Studies shall cover the realistic worst case situation, and the duration necessary for observation of potential leaching, taking into account the soil type, climatic conditions, the application rate and the frequency and period of application.
Študije zajemajo realno najslabše možne razmere in čas, ki je potreben za opazovanje možnega izpiranja, pri čemer se upoštevajo vrsta tal, podnebne razmere, odmerek ter pogostost in obdobje nanašanja.
The decision whether field leaching studies are to be carried out, as an experimental outdoor study in the framework of a tiered leaching assessment scheme shall take into account the calculated PECGW and the results of degradation and mobility studies.
Pri odločanju o izvedbi terenskih študij o izpiranju, pri čemer se izvedejo kot eksperimentalna študija na prostem v okviru večstopenjskega sistema ocenjevanja izpiranja, se upoštevajo izračunani PECGW ter rezultati študij o razgradnji in mobilnosti.
These studies shall be performed unless it is possible to extrapolate from data obtained on the active substance and metabolites, breakdown and reaction products in accordance with the requirements set out in point 7.1.4.3 of Part A of the Annex to Regulation (EU) No 283/2013.
Te študije se izvedejo le, kadar podatkov ni mogoče ekstrapolirati iz podatkov o aktivni snovi in metabolitih ter razgradnih in reakcijskih produktih, pridobljenih v skladu z zahtevami iz točke 7.1.4.3 dela A Priloge k Uredbi (EU) št. 283/2013.
Studies shall cover the realistic worst case situation, taking into account the soil type, climatic conditions, the application rate and the frequency and period of application.
Študije zajemajo realno najslabše možne razmere, pri čemer se upoštevajo vrsta tal, podnebne razmere, odmerek ter pogostost in obdobje nanašanja.
PECS estimations shall relate both to a single application at the highest rate of application for which authorisation is sought, and to the maximum number at the shortest interval and highest rates of application for which authorisation is sought, and shall be expressed in terms of mg of active substance per kg of dry soil.
Pri ocenah vrednosti PECS se upoštevata enkratni nanos z najvišjim odmerkom, za katerega se zahteva registracija, ter največje število v najkrajšem razmiku in z najvišjimi odmerki, za katere se zahteva registracija, pri čemer se izrazijo v mg aktivne snovi na kg suhih tal.
The factors which shall be considered in making PECS estimations relate to direct and indirect application to soil, drift, run off, and leaching and include processes such as volatilisation, adsorption, hydrolysis, photolysis, aerobic and anaerobic degradation.
Pri pripravi ocen PECS se upoštevajo neposredni in posredni nanos na tla, zanašanje, odtekanje, izpiranje, izhlapevanje, adsorpcija, hidroliza, fotoliza ter aerobna in anaerobna razgradnja.
Appropriate soil layer depths shall be used depending on the application method and soil cultivation.
Glede na metodo nanašanja in obdelavo tal se uporabi ustrezna globina plasti tal.
Where ground cover is present at time of application, the impact of crop interception in reducing soil exposure may be included in estimations.
Kadar so med nanosom tla pokrita, se lahko pri ocenah upošteva vpliv intercepcije kultur na zmanjšanje izpostavljenosti tal.
Initial PECS, immediately after application, shall be provided for the active substance, metabolites, breakdown and reaction products.
Navedejo se začetne vrednosti (PECS) neposredno po nanosu za aktivno snov, metabolite ter razgradne in reakcijske produkte.
Appropriate short-term and long-term PECS calculations (time weighted averages) shall be provided for the active substance, metabolites, breakdown and reaction products with respect to data from ecotoxicological studies.
Navedejo se ustrezni izračuni kratkoročnih in dolgoročnih PECS (časovno tehtana povprečja) za aktivno snov, metabolite ter razgradne in reakcijske produkte, pri čemer se upoštevajo podatki iz ekotoksikoloških študij.
Calculation of plateau concentrations in soil shall be provided where on the basis of soil dissipation studies it is established that DisT90 > one year, and where repeated application is envisaged, whether in the same growing season or in succeeding years.
Izračun največjih koncentracij v tleh se navede, kadar je na podlagi študij o razpadu v tleh ugotovljeno, da je DisT90 > eno leto, in kadar so predvideni večkratni nanosi v isti rastni dobi ali naslednjih letih.
The persistence and behaviour of plant protection products in open water (freshwater, estuarine and marine) shall be investigated unless it is possible to extrapolate from data obtained on the active substance and metabolites, breakdown and reaction products in accordance with the requirements set out in point 7.2.2.2 of Part A of the Annex to Regulation (EU) No 283/2013.
Obstojnost in obnašanje fitofarmacevtskih sredstev v odprtih vodah (sladka voda, rečna ustja in morska voda) se preučita le, kadar podatkov ni mogoče ekstrapolirati iz podatkov o aktivni snovi in metabolitih ter razgradnih in reakcijskih produktih, pridobljenih v skladu z zahtevami iz točke 7.2.2.2 dela A Priloge k Uredbi (EU) št. 283/2013.
The test shall be reported unless the applicant shows that contamination of open water will not occur.
Preskus se navede, razen če vlagatelj dokaže, da ne bo prišlo do onesnaženja odprtih voda.
The persistence and behaviour of plant protection products in aquatic systems shall be investigated unless it is possible to extrapolate from data obtained on the active substance and metabolites, breakdown and reaction products in accordance with the requirements set out in point 7.2.2.3 of Part A of the Annex to Regulation (EU) No 283/2013.
Obstojnost in obnašanje fitofarmacevtskih sredstev v vodnih sistemih se preučita le, kadar podatkov ni mogoče ekstrapolirati iz podatkov o aktivni snovi in metabolitih ter razgradnih in reakcijskih produktih, pridobljenih v skladu z zahtevami iz točke 7.2.2.3 dela A Priloge k Uredbi (EU) št. 283/2013.
The test shall be reported unless the applicant shows that contamination of surface water will not occur.
Preskus se navede, razen če vlagatelj dokaže, da ne bo prišlo do onesnaženja površinskih voda.
If more than 90% of the active substance is degraded before the period of 100 days expires, the test duration may be shorter.
Če se pred koncem 100-dnevnega obdobja razgradi več kot 90 % aktivne snovi, je lahko preskus krajši.
The degradation pattern of potentially relevant metabolites occurring within the water/sediment study shall be established by extension of the study for the active substance, when it is not possible to extrapolate from point 7.2.2.3 of Part A of the Annex to Regulation (EU) No 283/2013.
Vzorec razgradnje potencialno relevantnih metabolitov v okviru študije o vodi/usedlini se določi z razširitvijo študije za aktivno snov, kadar ni možna ekstrapolacija iz točke 7.2.2.3 dela A Priloge k Uredbi (EU) št. 283/2013.
If photochemical degradation is of importance, a water/sediment study under influence of a light/dark regime may additionally be reported.
Če je pomembna fotokemijska razgradnja, se lahko navede tudi študija o vodi/usedlini pod vplivom svetlobnega režima.
The groundwater contamination routes shall be defined taking into account relevant agricultural, plant health, and environmental (including climatic) conditions.
Opredelijo se poti onesnaženja podtalnice ob upoštevanju ustreznih razmer kmetijske pridelave, zdravstvenega varstva rastlin in okolja (vključno s podnebnimi razmerami).
PECGW estimations shall relate to the maximum number and highest rates of application, at the shortest interval, and to the time of application for which authorisation is sought.
Pri ocenah PECGW se upoštevajo največje število nanosov in najvišji odmerki v najkrajšem razmiku ter čas nanosa, za katerega se zahteva registracija.
Relevant EU groundwater models shall be run.
Upoštevajo se ustrezni modeli EU za podtalnico.
Where specific crops and circumstances are relevant, specific scenarios for typical use situations for the regions of use, for the respective crop or other situation of use shall be used.
Kadar so pomembne posamezne kulture in okoliščine, se uporabijo posamezni scenariji za okoliščine običajne uporabe za regije, v katerih se uporabljajo, za zadevno kulturo ali drugo okoliščino uporabe.
In case the behaviour in soil is dependent on soil parameters, respective parameters on degradation and adsorption in soil (DegT50 and Koc values) reflecting this dependency shall be used.
Kadar je obnašanje v tleh odvisno od parametrov tal, se uporabijo ustrezni parametri o razgradnji in adsorpciji v tleh (vrednosti DegT50 in Koc), ki izražajo takšno odvisnost.
If identified metabolites, breakdown or reaction products are found to occur in concentrations above 0,1 μg/L in the leachate, an assessment of their relevance shall be required.
Kadar je ugotovljeno, da koncentracije opredeljenih metabolitov, razgradnih ali reakcijskih produktov v izcedni vodi presegajo 0,1 μg/l, je treba oceniti njihovo relevantnost.
Suitable estimations (calculations) of predicted environmental concentration in groundwater PECGW, of active substance shall be submitted, unless it is clearly evident from the data on degradation or adsorption, taking worst case values, that leaching would be negligible under the intended areas of use.
Predložijo se primerne ocene (izračuni) predvidene okoljske koncentracije aktivne snovi v podtalnici PECGW, razen če podatki o razgradnji ali adsorpciji ob upoštevanju najslabših možnih vrednosti jasno kažejo, da bi bilo izpiranje na predvidenih področjih uporabe zanemarljivo.
For all metabolites, breakdown or reaction products identified as a part of the residue definition for risk assessment with respect to groundwater (see point 7.4.1 of Part A of the Annex to Regulation (EU) No 283/2013) a PECGW calculation shall be required for assessing their relevance.
Za oceno relevantnosti vseh metabolitov, razgradnih ali reakcijskih produktov, določenih v okviru opredelitve ostankov za oceno tveganja v zvezi s podtalnico (glej točko 7.4.1 dela A Priloge k Uredbi (EU) št. 283/2013), je treba zagotoviti izračun PECGW.
Where identified metabolites, breakdown or reaction products are found to occur in concentrations above 0,1 μg/L in the leachate, an assessment of their relevance shall be required.
Kadar je ugotovljeno, da koncentracije opredeljenih metabolitov, razgradnih ali reakcijskih produktov v izcedni vodi presegajo 0,1 μg/l, je treba oceniti njihovo relevantnost.
The need to perform additional field tests and the type and conditions of the tests to be performed shall be discussed with the national competent authorities.
Potreba po izvedbi dodatnih terenskih preskusov ter vrsta in pogoji preskusov, ki jih je treba izvesti, se preučijo skupaj z nacionalnimi pristojnimi organi.
The surface water and sediment contamination routes shall be defined taking into account relevant agricultural, plant health, and environmental (including climatic) conditions.
Opredelijo se poti onesnaženja površinskih voda in usedlin ob upoštevanju ustreznih razmer kmetijske pridelave, zdravstvenega varstva rastlin in okolja (vključno s podnebnimi razmerami).
Suitable estimations (calculations) of predicted environmental concentration in surface water PECSW and sediment PECSED of active substance shall be submitted, unless the applicant shows that contamination will not occur.
Predložijo se primerne ocene (izračuni) predvidene okoljske koncentracije v površinskih vodah PECSW in usedlinah PECSED za aktivno snov, razen če vlagatelj dokaže, da ne bo prišlo do onesnaženja.
PECSW and PECSED estimations shall relate to the maximum number and highest rates of application, at the shortest interval, for which authorisation is sought, and be relevant to ditches, ponds, and streams.
Pri ocenah PECSW in PECSED se upoštevajo največje število nanosov in najvišji odmerki v najkrajšem razmiku, za katere se zahteva registracija, pri čemer morajo vključevati jarke, ribnike in potoke.
Relevant EU surface water modelling tools shall be run.
Upoštevajo se ustrezna orodja za modeliranje EU za površinske vode.
The factors which shall be considered in making PECSW and PECSED estimations relate to direct application to water, drift, run-off, discharge via drains and atmospheric deposition, and include processes such as volatilisation, adsorption, advection, hydrolysis, photolysis, biodegradation, sedimentation and re-suspension, and transfer between water and sediment.
Pri pripravi ocen PECSW in PECSED se upoštevajo neposreden nanos v vodo, zanašanje, odtekanje, odvajanje preko drenažnih kanalov in jarkov, usedanje iz zraka, izhlapevanje, adsorpcija, advekcija, hidroliza, fotoliza, biorazgradnja, sedimentacija in resuspenzija ter prenos med vodo in usedlino.