natgillin/translations-raw huggingface dataset:
Produktdata for ovnrensemiddel indeholdende N-methyl-2pyrrolidon
Product data for oven cleaners containing N-methyl-2pyrrolidone
Spray med drivmiddel (aerosolspray)
Spray with propellant (aerosol spray)
Ryst dåsen godt og sprøjt i en afstand af ca. 25 cm i et jævnt lag i den kolde ovn/grill på alle flader og riste.
Shake the can well and spray at a distance of 25 cm in an even coat into the cold barbecue/oven on all surfaces and grills.
På øvrige genstande sprøjtes også i en afstand på 25 cm. Vask skummet af med en fugtig svamp eller klud.
Other objects are also sprayed from a distance of 25 cm. Wash away the foam with a damp sponge or cloth.
Estimeres til 0,8 kg.L-1 .
Estimated to 0.8 kg.L-1 .
Brugt mængde pr. rengøring
Used amount per cleaning
Respirationshastighed (let arbejde) IHair
Respiration velocity (light work)
N-Methyl-2-pyrrolidon kan optages gennem huden.
N-Methyl-2-pyrrolidone can be absorbed through the skin.
Det er derfor nødvendigt at medregne hudoptagelse ved beregning af den systemiske dosis.
Therefore, it is necessary to include skin absorption when calculating the systemic dose.
Det antages, at produktet anvendes en gang ugentligt til rengøring af ovn, hvilket er udtryk for et worst-case forbrug.
It is assumed that the product is used once a week for cleaning of oven, which is an expression of a worst-case consumption.
Da N-methyl-2-pyrrolidon er tungtflygtigt med et damptryk på 70 Pa ved 25 °C, antages det, at kun 1 % fordamper under brugen og kan indåndes.
As N-methyl-2-pyrrolidone is heavily volatile with a vapour pressure of 70 Pa at 25 °C, it is assumed that only 1 % evaporates during use and may be inhaled.
For produkter i aerosoldåse med drivgas antages det, at 60 % af produktet forbliver i luften /37/, og at 10 % af denne mængde kommer i kontakt med huden, dvs. 6 % af den anvendte mængde.
For products in aerosol cans with a propellant, it is assumed that 60 % of the product stays in the air /37/, and that 10 % of this amount comes into contact with the skin, i.e. 6 % of the used amount.
Optagelse af N-methyl-2pyrrolidon gennem huden sættes til 100 % (worst-case).
Absorption of N-methyl-2pyrrolidone through the skin is set to 100 % (worst-case).
Resultaterne af eksponeringsberegningen er vist i tabel 6.16.
The results of the exposure calculation are shown in Table 6.16.
Ved risikovurderingen sammenlignes de beregnede eksponeringsværdier med udledte referenceværdier i tabel 6.17.
When risk assessing, the calculated exposure values are compared with the drawn reference values in Table 6.17.
Beregnede eksponeringsdata for N-methyl-2-pyrrolidon
Calculated exposure data for N-methyl-2-pyrrolidone
Dosis ved indånding
Dose by inhalation
Dosis ved hudkontakt
Dose by skin contact
1) Det er antaget, at kun 1 % af N-methyl-2-pyrrolidon fordamper.
1) It is assumed that only 1 % of N-methyl-2-pyrrolidone evaporates.
Systemisk effekt, korttidseksponering
Systemic effect, short-term exposure
Systemisk effekt, gentagen eksponering
Systemic effect, repeated exposure
6.3.2.1 Hudirritation Den estimerede hudbelastning med N-methyl-2-pyrrolidon er 0,1 mg.cm
6.3.2.1 Skin irritation The estimated dermal load with N-methyl-2-pyrrolidone is 0.1 mg.cm
N-Methyl-2-pyrrolidon optages let gennem huden.
N-Methyl-2-pyrrolidone is readily absorbed through the skin.
Bidraget til den systemiske eksponering fra hudoptagelse er estimeret til 0,17 mg.kgbw
The contribution to the systemic exposure from skin absorption is estimated to 0.17 mg.kgbw
. Bidraget til den systemiske eksponering fra indånding af dampe af N-methyl-2-pyrrolidon er beregnet til 0,0017 mg.kgbw
. The contribution to the systemic exposure from inhalation of vapours of N-methyl-2-pyrrolidone is calculated to 0.0017 mg.kgbw
Hvis den beregnede eksponering sammenlignes med den udledte referenceværdi RVkronisk på 105 mg.kgbw
If the calculated exposure is compared to the drawn reference value RVchronic of 105 mg.kgbw
Det vurderes, at der ikke er risiko for akutte eller kroniske effekter ved denne anvendelse af N-methyl-2pyrrolidon.
It is assessed that there is no risk of acute or chronic effects when using N-methyl2-pyrrolidone this way.
Et rengøringsprodukt til ovne (produkt nr. 5) er udvalgt som repræsentant for produkter, der indeholder DPGME.
A cleaning product for ovens (product no. 5) has been selected to represent the products containing DPGME.
Produktet er et ovnrensemiddel i en dåse med pumpe.
The product is an oven cleaner in a can with a pump.
Tabel 6.18 og 6.19 viser de parametre, der ligger til grund for beregning af eksponering for DPGME.
Tables 6.18 and 6.19 show the parameters, which form the basis of the calculation of exposure to DPGME.
Produktdata for produkt til ovnrensemiddel indeholdende DPGME Produkttype
Product data for an oven cleaning product containing DPGME Product type
Gel i pumpeflaske
Gel in a pump bottle
Spray gel på ovnens overflader.
Spray the gel on the surfaces of the oven.
Lad gelen virke i 2-4 timer.
Leave the gel to work for 2-4 hours.
Ikke oplyst Koncentration i produktet (Fcprod) 0,13 (13 %)
Not informed Concentration in product (Fcprod) 0.13 (13 %)
Parametre anvendt til beregning af eksponering for DPGME Parameter
Parametres used for the calculation of exposure to DPGME Parametre
I det følgende vurderes risiko ved indånding, hudoptagelse og den totale eksponering ved beregning af MOE-værdier for disse eksponeringsveje for
In the following, the risk of inhalation, skin absorption and the total exposure are assessed by calculating MOE-values for these exposure routes for DPGME.
Da DPGME er tungt flygtigt med et damptryk på ca. 37 - 60 Pa ved 20 °C, antages det, at kun 1 % DPGME fordamper under brugen og kan indåndes.
As DPGME is heavily volatile with a vapour pressure of approx. 37 - 60 Pa at 20 °C, it is assumed that only 1 % DPGME evaporates during use and may be inhaled.
For produkter i pumpesprayflaske antages det, at 20 % af produktet forbliver i luften som sprøjtetåge /37/ og at 10 % kommer i kontakt med huden, dvs. 2 % af den anvendte mængde.
For products in pump spray bottles, it is assumed that 20 % of the product stays in the air as spray mist /37/, and that 10 % of this amount comes into contact with the skin, i.e. 2 % of the used amount.
Optagelse af DPGME over huden sættes til 100 % (worst-case).
Absorption of DPGME through the skin is set to 100 % (worst-case).
Beregnede eksponeringer for DPGME
Calculated exposures to DPGME
Ligning 6.5 0,031 mg.kgbw
Equation 6.5 0.031 mg.kgbw
1) Det er forudsat, at kun 1 % af DPGME fordamper.
1) It is assumed that only 1 % of DPGME evaporates.
2) Det er forudsat, at 20 % af produktet forekommer som sprøjtetåge i luften /37/,
2) It is assumed that 20 % of the product is found in the air as spray mist /37/,
Hudirritation Den estimerede hudbelastning med DPGME er 0,018 mg.cm
Skin irritation The estimated dermal load with DPGME is 0.018 mg.cm
. Der er ikke fundet kvantitative data, som muliggør en vurdering af eventuel hudirritation.
. No quantitative data were found, which would have enabled an assessment of possible skin irritation.
DPGME optages let gennem huden.
DPGME is readily absorbed through the skin.
Luftkoncentrationen af DPGME er beregnet til 3,3 mg.m-3
The concentration of air of DPGME is calculated to 3.3 mg.m-3
3. Det er ca. 135 gange lavere end den koncentration, som har medført slimhindeirritation hos mennesker (MOE = 135).
3. This is approx. 135 times lower than the concentration that caused irritation of the mucous membranes in humans (MOE = 135).
Det vurderes, at der ikke er risiko for slimhindeirritation ved denne anvendelse af DPGME.
It is assessed that there is a risk of irritation of the mucous membranes when using DPGME this way.
Bidraget til den systemiske eksponering er estimeret til 0,03 mg.kgbw
The contribution to the systemic exposure from skin absorption is estimated to 0.03 mg.kgbw
Sammenlignes denne beregnede eksponering med den udledte referenceværdi RVakut på 1035 mg.kgbw
. When comparing the calculated exposure to the drawn reference value RVacute of 1035 mg.kgbw
Det vurderes, at der ikke er risiko for akutte eller kroniske effekter ved denne anvendelse af DPGME.
It is assessed that there is no risk of acute or chronic effects when using DPGME this way.
6.3.4 Petroleumdestillat i rengøringsmiddel til glaskeramiske plader
6.3.4 Petroleum distillate in cleaners for ceramic cooktops
Et rengøringsprodukt til glaskeramiske plader (produkt nr. 3) er udvalgt som repræsentant for produkter, der indeholder petroleumsdestillat.
A cleaning product for ceramic cooktops (product no. 3) has been selected to represent the products containing petroleum distillate.
Produktet påføres med klud.
The product is applied with a cloth.
Tabel 6.22 og 6.23 viser de parametre, der ligger til grund for beregning af eksponering for petroleumsdestillat.
Tables 6.22 and 6.23 show the parameters, which form the basis of the calculation of exposure to petroleum distillate.
Til risikovurderingen benyttes de udledte RVakut og RVkronisk for mineralsk terpentin.
For the risk assessment, the drawn RVacute and RVchronic are used for white spirit.
Produktdata for produkt til glaskeramiske plader indeholdende petroleumsdestillat
Product data for a cleaning product for ceramic cooktops containing petroleum distillate
I det følgende vurderes risiko ved slimhindeeksponering og risiko ved systemisk eksponering ved indånding.
In the following, the risk of exposure of the mucous membranes and the risk of systemic exposure by inhalation are assessed.
Der er ikke fundet kvantitative data for petroleumdestillats optagelse gennem huden, men den vides at være meget begrænset gennem intakt hud.
No quantitative data were found for absorption through skin of petroleum distillates, but it is known to be very limited through intact skin.
Det vurderes, at optagelse gennem huden er negligeabel den korte kontakttid taget i betragtning.
It is assessed that absorption through the skin is negligible considering the short contact time.
Bidraget til den systemiske eksponering er derfor sat til nul.
The contribution to the systemic exposure has therefore been set to naught.
1) Det er forudsat, at kun 1 % af indholdet af petroleumdestillat fordamper.
1) It is assumed that only 1 % of the petroleum distillate evaporates.
3) Petroleumdestillat trænger ikke igennem intakt hud.
3) Petroleum distillate does not penetrate intact skin.
Hudirritation Den estimerede hudbelastning med petroleumdestillat er 0,019 mg.cm
Skin irritation The estimated dermal load with petroleum distillate is 0.019 mg.cm
Petroleumdestillat kan affedte og udtørre huden og dermed medføre hudirritation.
Petroleum distillate may degrease and dry out the skin and thus cause skin irritation.
Handsker bør derfor anvendes under brug af produktet.
Gloves should be worn during use of the product.
Slimhindeeksponering Luftkoncentrationen af petroleumdestillat er beregnet til 3,5 mg.m-3
Exposure of the mucous membranes The concentration of air of petroleum distillate is calculated to 3.5 mg.m-3
3. Det er ca. 170 gange mindre end den koncentration, som har medført øjenirritation hos mennesker (MOE = 170).
3. This is approx. 170 times lower than the concentration that caused eye irritation in humans (MOE = 170).
Det vurderes, at der ikke er risiko for slimhindeirritation ved denne anvendelse af petroleumdestillat.
It is assessed that there is no risk of irritation of the mucous membranes when using petroleum distillate this way.
Der er ikke fundet kvantitative data for petroleumdestillats optagelse gennem huden, men det vurderes, at optagelsen er meget begrænset gennem intakt hud.
No quantitative data were found for the absorption through skin of petroleum distillate, but it is assessed that the absorption is very limited through intact skin.
Bidraget til den systemiske eksponering fra indånding af dampe af petroleumdestillat er beregnet til 0,0070 mg.kgbw
The contribution to the systemic exposure from inhalation of vapours of petroleum distillate is calculated to 0.0070 mg.kgbw
Det vurderes, at der ikke er risiko for akutte eller kroniske effekter ved denne anvendelse af petroleumdestillat.
It is assessed that there is no risk of acute or chronic effects when using petroleum distillate this way.
6.3.5 Mineralsk terpentin i stålplejemiddel
6.3.5 White spirit in stainless steel care products
Et stålplejemiddel (produkt nr. 20) er udvalgt som repræsentant for produkter, der indeholder mineralsk terpentin.
A stainless steel care product (product no. 20) has been selected to represent the products containing white spirit.
Tabel 6.26 og 6.27 viser de parametre, der ligger til grund for den beregnede eksponering for mineralsk terpentin.
Tables 6.26 and 6.27 show the parametres, which form the basis of the calculation of exposure to white spirit.
Parametre anvendt til beregning af eksponering for mineralsk terpentin Parameter
Parametres used for the calculation of exposure to white spirit Parametre
5 g (fundet ved praktiske forsøg)
5 g (found during practical testing)
Mineralsk terpentin er relativt tungt flygtigt med et damptryk på ca. 600 Pa ved 25 °C.
White spirit is relatively heavily volatile with a vapour pressure of approx. 600 Pa at 25 °C.
Sammenhængen er tilnærmelsesvis lineær ved lave damptryk.
The connection is approximately linear at low vapour pressure.
Damptrykket for mineralsk terpentin er ca. 10 gange højere end damptrykket for de tre øvrige opløsningsmidler, der er vurderet i denne rapport.
The vapour pressure for white spirit is approx. 10 times higher than the vapour pressure for the three other solvents assessed in this report.
Mineralsk terpentin estimeres derfor at fordampe ca. 10 gange hurtigere end disse.
White spirit is therefore estimated to evaporate approx. 10 times faster than these.
Som en 'realistisk worst-case' i de efterfølgende eksponeringsberegninger er det antaget, at der fordamper 10 % mineralsk terpentin under brugen.
As a realistic worst-case in the following exposure calculations, it is assumed that 10 % white spirit evaporates during use.
Der er ikke fundet kvantitative data for mineralsk terpentins optagelse gennem huden, men den vides at være begrænset gennem intakt hud.
No quantitative data were found for absorption through skin of white spirit, but it is known to be very limited through intact skin.
1) Det er forudsat, at 10 % af indholdet af mineralsk terpentin fordamper.
1) It is assumed that only 10 % of the white spirit evaporates.
3) Mineralsk terpentin trænger ikke igennem intakt hud.
3) White spirit does not penetrate intact skin.
Optagelse gennem huden er sat til 0 %.
Absorption through skin is set to 0 %.
Hudirritation Den estimerede hudbelastning med mineralsk terpentin er 0,082 mg.cm
Skin irritation The estimated dermal load with white spirit is 0.082 mg.cm
Mineralsk terpentin kan affedte og udtørre huden og dermed medføre hudirritation.
White spirit may degrease and dry out the skin and thus cause skin irritation.
Slimhindeeksponering Luftkoncentrationen af mineralsk terpentin er beregnet til 150 mg.m-3
Exposure of the mucous membranes The concentration of air of white spirit is calculated to 150 mg.m-3
3. Det er ca. 4 gange lavere end den koncentration, som har medført øjenirritation hos mennesker.
3. This is approx. 4 times lower than the concentration that caused eye irritation in humans.
Mineralsk terpentins slimhindeirritation afhænger af indholdet af naphtheniske og aromatiske carbonhydrider.
The irritating effect of white spirit to the mucous membranes depends on the contents of naphthenic and aromatic hydrocarbons.
Hvis den anvendte type mineralsk terpentin kun indeholder små mængder af især aromatiske carbonhydrider vil slimhindeirritation være væsentligt begrænset ved denne anvendelse af mineralsk terpentin.
If the used type of white spirit only contains small amounts of especially aromatic hydrocarbons, irritation of the mucous membranes will be considerably limited when using white spirit this way.
Der er ikke fundet kvantitative data for mineralsk terpentins optagelse gennem huden, men det vurderes at optagelsen er meget begrænset gennem intakt hud.
No quantitative data were found for the absorption through skin of white spirit, but it is assessed that the absorption is very limited through intact skin.
Bidraget til den systemiske eksponering fra indånding af dampe af mineralsk terpentin er beregnet til 0,088 mg.kgbw
The contribution to the systemic exposure from inhalation of vapours of white spirit is calculated to 0.088 mg.kgbw
. Sammenlignes denne beregnede eksponering med den udledte referenceværdi RVakut på 10 mg.kglgv
. When comparing the calculated exposure to the drawn reference value RVacute of 10 mg.kgbw
Det vurderes, at der vil være en risiko for kroniske effekter ved denne anvendelse af mineralsk terpentin gennem en lang periode.
It is assessed that there will be a risk of chronic effects when using white spirit for a long period of time.
6.4 Miljøvurdering af udvalgte stoffer
6.4 Environmental assessment of selected substances
N-methyl-2-pyrrolidon vurderes at være fuldstændigt bionedbrydelig på baggrund af resultater opnået i forskellige test for bionedbrydelighed /12/.
N-methyl-2-pyrrolidone is assessed to be completely biodegradable on the basis of results from various tests for biodegradability /12/.
Der er ikke fundet data for den anaerobe bionedbrydelighed.
No data were found for the anaerobic biodegradability.
Disse data indikerer, at DPGME har en lav akut giftighed overfor vandlevende organismer med EC/LC50-værdier > 100 mg.L-1
indicate that DPGME has low acute toxicity for aquatic organisms with EC/LC50-values > 100 mg.L-1
i test med krebsdyr og fisk /12/.
in tests with crustacean and fish /12/.
Med en estimeret log POW-værdi < 0 vurderes stoffet at være ikke bioakkumulerbart.
With an estimated log POW-value < 0 the substance is assessed to be not bioaccumulable.
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 %