natgillin/translations-raw huggingface dataset:
DPGME vurderes på baggrund af ovenstående data ikke at være til fare for miljøet. 
On the basis of the above data, DPGME is assessed to constitute no risk to the environment.
Petroleumsdestillater er ikke fuldstændigt bionedbrydelige i standard test for let bionedbrydelighed /12/. 
Petroleum distillates are not completely biodegradable in standard tests for ready biodegradability /12/.
Petroleumsdestillater kan betegnes som giftige over for vandlevende organismer med EC/LC50-værdier for akut toksicitet mellem 1-10 mg.L-1 
Petroleum distillates may be toxic to aquatic organisms with EC/LC50-values for acute toxicity between 1 - 10 mg.L-1
i standardtest med alger, krebsdyr og fisk /12, 13/. 
in standard tests with algae, crustacean and fish /12, 13/.
Med estimerede log POW-værdier mellem 3,3-8,7 kan petroleumsdestillater betegnes som potentielt bioakkumulerbare. 
With estimated log POWvalues between 3.3 and 8.7 petroleum distillates are potentially bioaccumulable.
Petroleumsdestillater burde således klassificeres som miljøfarlige (N) med R51/53 (giftig for organismer der lever i vand, kan forårsage uønskede langtidsvirkninger i vandmiljøet). 
Petroleum distillates should thus be classified as Dangerous for the environment (N) with R51/53 (Toxic to aquatic organisms, may cause long-term adverse effects in the aquatic environment.).
I kapitel 7 gives en nærmere vurdering af effekten af petroleumsdestillater i vandmiljøet. 
A more detailed assessment of the effect of petroleum distillates in the aquatic environment is given in Chapter 7.
Mineralsk terpentin vurderes på baggrund af data for petroleumsdestillater og naphta (råolie), hydrogenbehandlet, tung /12/ at være ikke fuldstændigt bionedbrydeligt og samtidig giftig over for vandlevende organismer med EC/LC50-værdier mellem 1-10 mg.L-1 
White spirit is assessed on the basis of data for petroleum distillates and naphtha (pertroleum), hydrogentreated, heavy /12/ to be not completely biodegradable and at the same time to be toxic to aquatic organisms with EC/LC50-values between 1 and 10 mg.L-1
. Med estimerede log POW-værdier mellem 2,1 - 6 kan mineralsk terpentin betegnes som potentielt bioakkumulerbart. 
. With estimated log POW-values between 2.1 and 6, white spirit is potentially bioaccumulable.
I kapitel 7 gives en nærmere vurdering af effekten af mineralsk terpentin i vandmiljøet. 
A more detailed assessment of the effect of white spirit in the aquatic environment is given in Chapter 7.
7.1 Vurdering af udvalgte stoffers effekter i vandmiljøet 
7.1 Substances selected for assessment of their effects in the aquatic environment
På baggrund af miljøvurderingen af de fire udvalgte stoffer i kapitel 6 blev henholdsvis petroleumsdestillater og mineralsk terpentin udvalgt til en nærmere vurdering af effekter i vandmiljøet, idet begge stoffer vurderedes at være giftige for vandlevende organismer og at kunne medføre uønskede langtidseffekter i vandmiljøet. 
Based on the environmental assessment in Chapter 6 of the four selected substances, petroleum distillates and white spirit, respectively, were selected for a more detailed assessment of effects in the aquatic environment as both groups of substances are considered to be toxic to aquatic organisms and to potentially cause adverse long-terms effects in the aquatic environment.
7.2 Skæbne af de kemiske stoffer i husholdningsprodukter 
7.2 Fate of the chemical substances in household products
Kemiske stoffer i rengøringsmidler, der anvendes i husholdningen, vil primært blive udledt til miljøet via renset spildevand fra kommunale renseanlæg. 
Chemical substances in cleaning agents used in households will primarily be discharged to the environment via treated waste water from municipal wastewater treatment plants (WWTP).
Rengøringsmidlerne skylles med vaskevandet ud til kloaknettet og ledes videre til renseanlæg. 
The cleaning agents are flushed with the slops to the sewage system and led to the WWTP.
I vandmiljøet vil forskellige biologiske og abiotiske fjernelsesprocesser ligeledes påvirke koncentrationen af de kemiske stoffer. 
Also in the aquatic environment, various biological and abiotic elimination processes influence the concentration of the chemical substances.
Dertil vil koncentrationen afhænge af hydrauliske parametre som f.eks. opblanding/fortynding og vandstrømningsforhold. 
Furthermore, the concentration will depend on hydraulic parameters as e.g. mixing/dilution and water flow conditions.
7.3 Totalt estimeret forbrug af petroleum og mineralsk terpentin i produkterne 
7.3 Estimated total consumption of petroleum distillates and white spirit in the products
Den årlige maksimale koncentration af petroleumsdestillater, der udledes som følge af anvendelse af produkter til glaskeramiske plader, er blevet estimeret ud fra følgende antagelser: 
The annual maximum concentration of petroleum distillates discharged as a result of the application of ceramic cooktop cleaners was estimated on the basis of the following assumptions:
• Produkterne indeholder i gennemsnit 0,25 liter 
• The products contained an average of 0.25 litres
• Densiteten af produkterne antages at være 1 g L 
• The density of the products was assumed to be 1 g/L
• Produkter til glaskeramiske plader udgør 65 % af det totale forbrug 
• Products for ceramic cooktops constituted 65 % of the total consumption
• 22 % af produkterne til glaskeramiske plader indeholder petroleum 
• 22 % of the products for ceramic cooktops contained petroleum
• Den gennemsnitlige koncentration af petroleum i disse produkter er 11 % 
• The average concentration of petroleum in these products was 11 %
Således estimeres det, at der årligt anvendes 2.360 kg petroleum i produkter til glaskeramiske plader. 
It was thus estimated that 2,360 kg petroleum are used in products for ceramic cooktops annually.
Den årlige maksimale koncentration af mineralsk terpentin, der udledes som følge af anvendelse af stålplejeprodukter, er blevet estimeret ud fra følgende antagelser: 
The annual maximum concentration white spirit discharged as a result of the application of stainless steel care products was estimated on the basis of the following assumptions:
• Maksimalt årligt salg af stålplejeprodukter: 100.000 produkter 
• Maximum annual sale of stainless steel care products: 100,000 products
• Andel af produkter der indeholder mineralsk terpentin: 75 % 
• Percentage of products containing white spirit: 75 %
• Gennemsnitligt indhold af mineralsk terpentin i produkterne: 25 % 
• Average content of white spirit in the products: 25 %
Således kan det estimeres, at der årligt anvendes 4.690 kg mineralsk terpentin i stålplejeprodukter. 
It was thus estimated that 4,690 kg white spirit are used in products for stainless steel care annually.
7.4 Beregning af predicted environmental concentration (PEC) og predicted no effect concentration (PNEC) 
7.4 Calculation of predicted environmental concentration (PEC) and predicted no effect concentration (PNEC)
Til estimering af den miljømæssige risiko ved udledning af petroleumsdestillater og mineralsk terpentin, sammenholdes den forventede miljømæssige koncentration (Predicted Environmental Concentration, PEC) med den koncentration af stoffet, ved hvilken, der ikke forventes effekter i vandmiljøet (Predicted No Effect Concentration, PNEC). 
For the estimation of the environmental risk of discharge of petroleum distillates and white spirit, the Predicted Environmental Concentration (PEC) was compared with the concentration of the substance, at which no effects are expected in the aquatic environment, the Predicted No Effect Concentration (PNEC).
Koncentrationen af stofferne i afledningen fra renseanlæg (PECstp) beregnes ud fra forbrugsmængderne (M) af stoffet, fjernelsesgraden i renseanlæggene (ffjernelse) og årligt afledt spildevand i Danmark (Q): 
The concentration of substances in the discharge from WWTPs (PECWWTP) was calculated on the basis of the amounts (M) of substance consumed, the degree of removal in the WWTPs (fremoval) and the annual amount of discharged waste water in Denmark (Q):
De beregnede PECstp-værdier fremgår af tabel 7.1 
Table 7.1 shows the calculated PECWWTP values.
Beregnede PEC-værdier Stof 
Calculated PEC values Substance
De højeste koncentrationer, der ikke forventes at medføre effekter i vandmiljøet, PNEC, beregnes ud fra data for stoffernes giftighed over for vandlevende organismer ved anvendelse af en ”vurderingsfaktor” (assessment factor), som beskrevet i EU's Technical Guidance Document /14/. 
The highest concentrations not expected to cause effects in the aquatic environment, PNEC, are calculated on the basis of data of the toxicity of the substances towards aquatic organisms using an assessment factor as described in the EU Technical Guidance Document /14/.
De beregnede PNEC-værdier for de udvalgte stoffer fremgår af tabel 7.2, se også afsnit 6.4.3. 
Table 7.2 gives the calculated PNEC values for the selected substances, see also subsection 6.4.3.
Beregnede PNEC-værdier Stof 
Calculated PNEC values Substance
Laveste effektværdi (mg L-1) 
Lowest effect value (mg L-1)
7.5 Beregning af risikokvotienter 
7.5 Calculation of risk quotients
RQ beregnes som PEC/PNEC. 
RQ is calculated as PEC/PNEC.
En risikokvotient > 1 angiver sandsynlighed for effekter i vandmiljøet. 
A risk quotient > 1 indicates probability of effects in the aquatic environment.
Der regnes med en standard fortyndingsfaktor på 10 efter udledning af renset spildevand til vandmiljøet. 
A dilution factor of 10 after discharge of treated waste water was assumed.
Således vil risikokvotienter mindre end 10 indikere, at der ikke vurderes at være risiko for uønskede effekter i vandmiljøet. 
Risk quotients < 10 will thus indicate that there is not considered to be any risk of adverse effects in the aquatic environment.
Af tabel 7.3 ses det, at risikokvotienten i afledningen fra renseanlæg for petroleumsdestillater ligger under 1, hvorfor dette stof ikke forventes at give anledning til effekter. 
Table 7.3 shows that the risk quotient for petroleum distillates in the discharge from WWTPs is below 1 for which reason petroleum distillates are not expected to cause any effects.
For mineralsk terpentin ligger risikokvotienten over 10, hvorfor udledning af dette stof kan forventes at medføre en risiko for effekter i vandmiljøet. 
For white spirit, the RQ is > 10 and discharge of this substance must be expected to cause a risk of effects in the aquatic environment.
For at vurdere effekten i vandmiljøet er der i det følgende udført simuleringer af fortyndingen og omsætningen af mineralsk terpentin i miljøet i et defineret eksponeringsscenarie. 
In order to assess the effect in the aquatic environment, simulations were made of the dilution and the transformation of white spirit in the environment of a defined exposure scenario.
Til beregning af koncentrationen (PEC) af de udvalgte kemiske stoffer anvendes en skæbnemodel, der beskriver nedbrydningen (biologisk nedbrydning, hydrolyse, fotolyse), fordampningen og sedimentationen. 
For the estimation of the concentration (PEC) of the selected chemical substances, a fate model describing degradation (biodegradation, hydrolysis, photolysis), evaporation and sedimentation was applied.
Samtlige processer er beskrevet ved et første ordens udtryk med hensyn til stofkoncentrationen. 
All processes were specified as first order expressions with regard to the substance concentration.
Procesbeskrivelserne er lagt ind i en såkaldt skabelon i modelleringsværktøjet ECOLAB, som er udviklet på DHI. 
The process specifications were entered into a template in the modelling tool ECOLAB developed by DHI.
Til beskrivelse af stoffernes transport knyttes skæbnemodellen til en hydraulisk model, som modellerer vandstrømninger i et defineret vandområde. 
In order to describe the transport of the substances, the fate model was linked to a hydraulic model, which models water flows in a defined water body.
I dette eksempel er den todimensionale model MIKE 21 anvendt (koncentrationen i dybden er antaget at være ensartet fordelt). 
In this example, the two-dimensional model MIKE 21 was applied (the vertical distribution was assumed to be uniformly distributed).
Lillebælt er endvidere her udvalgt som et repræsentativt eksponeringsscenario, der beskriver kystnære vandområder i Danmark. 
Furthermore, the Little Belt was chosen as a representative exposure scenario describing coastal areas in Denmark.
Området, som modellen dækker, er på ca. 35 km  50 km. 
The area covered by the model was approx. 35 km  50 km.
For at sikre at simuleringen når en form for ligevægt, er der anvendt en simuleringsperiode på 2 måneder. 
In order to ensure that the simulation attained some kind of equilibrium, a simulation period of 2 months was applied.
De vejrbetingelser, som er observeret den første uge af april 2004, blev anvendt gentagne gange (ca. 10) i simuleringen. 
The weather conditions observed in the first week of April 2004 were repeatedly applied (approx. 10 times) in the simulation.
Karakteristik af renseanlæg med udløb i Lillebælt Kolding Middelfart Fredericia Vejle Juelsminde 
Characteristics of WWTPs discharging into the Little Belt Kolding Middelfart Fredericia Vejle Juelsminde
MBNDK MBNDK MBNDK MBNDK MBNDK * M: mekanisk; B: biologisk; N: nitrifikation; D: denitifikation; K: kemisk udfældning. 
MBNDC MBNDC MBNDC MBNDC MBNDC * M: mechanical; B: biological; N: nitrification; D: denitrification; C: chemical precipitation
Placering af udløb fra renseanlæg, Lillebælt 
Location of discharges from WWTPs into the Little Belt
Således beregnes PEC (Predicted Environmental Concentration) for de udvalgte kemiske stoffer ved at koble skæbnen af de kemiske stoffer i renseanlæg og i vandmiljøet med strømningsforholdene i Lillebælt. 
PEC (Predicted Environmental Concentration) for the selected chemical substances was thus estimated by linking the fate of the chemical substances in WWTP and the aquatic environment with the flow behaviour of the Little Belt.
PECværdierne sammenholdes med stoffernes PNEC (Predicted No Effect Concentration), som er den højeste koncentration, ved hvilken der ikke forventes uønskede effekter i vandmiljøet, og der beregnes en risikokvotient (RQ = PEC/PNEC) for stofferne efter udledning til vandmiljøet. 
The PEC values were related to the PNEC (Predicted No Effect Concentration) of the substances, which is the highest concentration at which no adverse effects in the aquatic environment are expected, and a risk quotient (RQ = PEC/PNEC) was estimated for the substances after discharge into the aquatic environment.
I løbet af simuleringsperioden er der stor variation i koncentrationerne af de kemiske stoffer i vandmiljøet, som følge af den naturlige variation i strømforholdene. 
During the simulation period, large variations in the concentrations of the chemical substances in the aquatic environment occur as a result of the natural variation in the flow behaviour.
Til vurdering af eventuelle akutte effekter er den maksimale koncentration af mineralsk terpentin gennem simuleringsperioden beregnet og sammenlignet med 10  PNEC, idet det generelt antages, at PNEC for akutte effekter er en faktor 10 højere end PNEC for kroniske effekter. 
For the assessment of potential acute effects, the maximum concentration of white spirit throughout the simulation period was estimated and compared with 10  PNEC as it is generally assumed that PNEC for acute effects is a factor of 10 higher than PNEC for chronic effects.
Det område af Lillebælt, hvor der er risiko for akutte effekter, er fundet til at være væsentligt mindre end det område, hvor der er risiko for kroniske effekter. 
The area of the Little Belt, in which there is a risk of acute effects, was found to be considerably smaller than the area, in which there is a risk of chronic effects.
I figur 7.2 ses de beregnede risikokvotienter (kroniske effekter), som er fundet som forholdet mellem det tidsvægtede gennemsnit af de beregnede koncentrationer og PNEC. 
Figure 7.2 shows the estimated risk quotients (chronic effects) found as the ratio of the timeweighted average of the estimated concentration to PNEC.
Risikokvotienter for kroniske effekter af mineralsk terpentin i 
Risk quotients for chronic effects of white spirit in the Little Belt.
I de resterende vandområder i Lillebælt-scenariet blev der ikke fundet risiko for uønskede effekter af mineralsk terpentin. 
In the other areas of the Little Belt scenario, no risk of adverse effects from white spirit was found.
Den indre del af Vejle fjord er karakteriseret af en begrænset vandudskiftning sammenlignet med de andre spildevandsudledninger i Lillebælt. 
The inner part of Vejle Bay is characterised by a limited water exchange compared with the other wastewater discharges into the Little Belt.
Det er således ikke overraskende, at der er størst sandsynlighed for effekter i netop dette område. 
It was thus not surprising that the highest probability of effects occurred in exactly this area.
Beregningerne er udtryk for en worst-case situation med et højt estimeret forbrug af stålplejeprodukter. 
The estimates express a worst-case situation with a high estimated consumption of stainless steel care products.
På baggrund af de simuleringer, der blev gennemført for Lillebælt, kan det således konkluderes, at udledningen af mineralsk terpentin kan medføre uønskede langtidseffekter i vandmiljøet i en begrænset nærzone omkring spildevandsudledninger, hvor området samtidig er karakteriseret af en begrænset vandudskiftning. 
Based on the simulations made for the Little Belt, it can be concluded that the discharge of white spirit may cause adverse long-term effects in the aquatic environment in a limited near zone around waste-water discharges when, at the same time, the area is characterised by a limited water exchange.
Der blev ikke fundet risikokvotienter > 1 for akutte effekter i Lillebælt (data ikke vist). 
No risk quotients > 1 were found for acute effects in the Little Belt (data not shown).
Ud fra de tilgængelige data om indholdsstofferne i produkter til rengøring af ovn, komfur og keramiske plader gives i det følgende en kort karakteristik af de enkelte produkttyper med fokus på produkternes indhold af kritiske stoffer. 
Based on the available data on the constituents in products for cleaning of ovens, cookers and ceramic cooktops, short characteristics of the individual product types are given below focussing on their contents of critical substances.
Ovnrensemidler på spray kan indeholde høje koncentrationer af opløsningsmidlet N-methyl-2-pyrrolidon, som er lokalirriterende (Xi, R36/38), og er endvidere, som nævnt, foreslået klassificeret som reproduktionsskadeligt (T; R61: kan være skadeligt for barnet under graviditeten). 
Spray oven cleaners may contain high concentrations of the solvent Nmethyl-2-pyrrolidone, which is irritant (Xi, R36/38) and which, as mentioned, should be classified as reproduction toxic (T; R61 May cause harm to the unborn child).
Eksponeringsberegninger for N-methyl-2-pyrrolidon har dog vist, at risikoen for effekter på sundhed og reproduktion vurderes at være minimal. 
Exposure estimations for N-methyl-2-pyrrolidone showed, however, that the risk of effects on health and reproduction is estimated to be minimal.
Det anbefales dog at undgå eksponering for N-methyl-2-pyrrolidon under graviditet. 
It is, however, recommended to avoid exposure to N-methyl-2pyrrolidone during pregnancy.
Ud fra de tilgængelige oplysninger vurderes ovnrensemidler på flydende form ikke at indeholde stoffer, der er skadelige for forbrugerens sundhed eller for miljøet. 
Based on the available information, liquid oven cleaners are not considered to contain substances that are harmful to consumer health or the environment.
8.2 Produkter til glaskeramiske kogeplader 
8.2 Products for ceramic cooktops
Enkelte af de indkøbte produkter til glaskeramiske kogeplader indeholder opløsningsmidlet petroleum, som kan være farligt for både sundhed og miljø. 
A few of the purchased products for ceramic cooktops contained the solvent petroleum, which may be hazardous to both health and the environment.
Eksponeringsberegninger har vist, at den sundhedsmæssige risiko ved anvendelsen af produkterne vurderes at være begrænset. 
Exposure estimations showed that the health risk from application of the products is estimated to be limited.
Udledningen af petroleumsdestillater til vandmiljøet som følge af brugen af produkterne vurderes ikke at give anledning til risiko for uønskede effekter. 
The discharge of petroleum distillates into the aquatic environment as a result of the application of the products is not considered to cause any risk of adverse effects.
Tre ud af fire indkøbte stålplejemidler vurderes at indeholde en form for mineralsk terpentin, som er farligt for både sundhed og miljø. 
Three of four purchased stainless steel care products are assessed to contain a form of white spirit, which is hazardous to both health and the environment.
Koncentrationen af dette stof i produkterne er ukendt, men vurderes på baggrund af informationer fundet i sikkerhedsdatablade for lignende produkter at ligge mellem 10 -  30 %. 
The concentration of this substance in the products is unknown but, based on information found in safety data sheets for similar substances, it was estimated to be 10 -  30 %.
To af produkterne er klassificerede som sundhedsskadelige, hvorfor koncentrationen af mineralsk terpentin i disse produkter sandsynligvis overstiger 10 %, som er den nedre koncentrationsgrænse for klassificering for sundhedsfare. 
As two of the products are classified as health hazardous, the concentration of white spirit in these products probably exceeds 10 %, which is the lower concentration limit for classification for health hazards.
Eksponeringsberegninger pegede på, at der kan være en sundhedsmæssig risiko forbundet med anvendelse af produkter, hvori der indgår en høj koncentration af mineralsk terpentin, hvis der ikke er tilstrækkelig ventilation. 
Exposure calculations indicated that there may be a health risk in using products with a high content of white spirit if there is not adequate ventilation.
På baggrund af en simulering af koncentrationen af mineralsk terpentin i spildevand, der udledes til Lillebælt, vurderes dette at kunne medføre effekter i en begrænset nærzone omkring spildevandsudledninger i områder karakteriseret af begrænset vandudskiftning. 
Based on a simulation of the concentration of white spirit in waste water discharged into the Little Belt, this substance is estimated to potentially cause effects in a limited near zone around waste-water discharges in areas characterised by a limited water exchange.
8.4 Produkter til rengøring af kogeplader og mikrobølgeovne Disse produkter vurderes ikke at indeholde stoffer i koncentrationer, som er skadelige for forbrugerens sundhed eller miljøet. 
8.4 Products for cleaning of cooktops and microwave ovens These products are not estimated to contain substances in concentrations harmful to consumer health or the environment.
9.1 Hovedkonklusioner fra kortlægningen 
9.1 Main conclusions from the survey
Resultatet af kortlægningen har givet en oversigt over hvilke kemiske stoffer, der typisk indgår i produkterne. 
The result of the survey gave an overview of the chemical substances that typically form part of the products.
Rengøringsmidler til ovn, komfur og keramiske plader indeholder typisk stoffer som tensider (nonioniske og anioniske tensider, fedtsyresæber), opløsningsmidler, surhedsregulerende midler (syrer, baser), slibe/polermidler, konserveringsmidler, silikoneforbindelser, fortykkelsesmidler og parfume. 
Cleaners for oven, cooker and ceramic cooktops typically contain substances as surfactants (non-ionic and anionic surfactants, fatty acid soaps), solvents, acidity regulating agents (acids, bases), abrasives/polishers, preservatives, silicone compounds, thickening agents and fragrance.
Sammensætningen varierer alt efter produktets anvendelsesområde og form. 
The compositions vary according to the application area and form.