natgillin/translations-raw huggingface dataset:
2, og det antages, at 100 % af alt formaldehyd absorberes, inden limen afvaskes, fx efter 1 time, ud fra Log Kow = 0,35.
2, and it is further assumed that 100 % formaldehyde is absorbed before the glue is washed off, e.g. after 1 hour based on Log Kow = 0,35.
Det skal dog bemærkes, at noget formaldehyd vil nå at fordampe grundet det høje damptryk.
It should be mentioned that some formaldehyde will evaporate due to the high vapour pressure.
Det antages, at en maksimal indtagen oral mængde ved fx at sutte på glimmerlim eller fingre er af samme størrelsesorden.
It is assumed that the maximum oral intake will be the same whether the child is sucking fingers or sucking on objects like glitter glue.
Baseret på NOAEL = 15 mg/kg/dag kan beregnes MOS = 15/0,022 = 676 ved optag gennem huden eller ved oralt optag.
Based on NOAEL = 15 mg/kg/day the safety margin can be calculated to MOS = 15/0,022 = 676 by skin absorption or by oral intake.
Dette svarer ca. til 9 gange under den kritiske referencedosis.
This corresponds to 9 times below the critical reference dose.
Stoffet bidrager imidlertid med en forøget risiko for kræftfremkaldende effekt samt en allergifremkaldende effekt.
The substance will give an increased risk of carcinogenic and allergenic effect.
Endvidere bidrager stoffet med et væsentligt bidrag til de andre kendte kilder for formaldehyd i danske hjem som fx spånplader, elektroniske produkter m.m.
Further it contributes to other known sources for formaldehyde in Danish homes, e.g. chipboards, electronic products etc.
For at kunne bedømme afdampning til indeklimaet præcist kræves forsøg i klimakamre, hvilket ikke er udført i nærværende projekt.
To assess the evaporations into the indoor climate it is necessary to carry tests out in climate chambers, which has not been effected in this project.
For at vurdere muligheden for inhalering af sundhedsskadelige mængder er i stedet vurderet et par worst cases, hvor alt stof antages at fordampe
To be able to assess the risk of inhalation of hazardous substances a number of worst case scenarios have been estimated, where it is assumed that all
Alternativt er vurderet den maksimale stofkoncentration i et lukket børneværelse uden cirkulation på 3 * 3 * 2 m = 18 m
Alternatively, the maximum substance concentration is estimated in a closed child's room with recirculation of 3 * 3 * 2 m = 18 m
Formaldehyd findes i glimmerlim, som anvendes i mængder af ca. 6 g/100 cm
Formaldehyde is found in glitter glue, which is used in amounts of approx. 6 g/100 cm
i koncentrationer op til 0,11 mg/g.
in concentrations of up to 0.11 mg/g.
3, vil formaldehydkoncentrationen af 6 g glimmerlim maksimalt kunne nå 0,04 mg/m
3, the formaldehyde concentration of 6 g glitter glue will be maximum reach 0.04 mg/m
3, hvilket er 10 gange under den arbejdshygiejniske grænseværdi og 4 gange under den anbefalede indeklimakoncentration.
3, which is 10 times below the TLV and 4 times below the recommended indoor climate value.
Det må derfor anbefales at sørge for god udluftning, hvis der arbejdes med glimmerlim i større mængder i små rum.
It is therefore recommended that the room is ventilated properly when working with large volumes of glitter glue.
2-ethoxyethanol findes i tuschpenne, som anvendes i mængder op til 0,1 g/100 cm
2-ethoxyethanol is found in marker pens, which is used in amounts up to 0.1 g/100 cm
i koncentrationer op til 19 mg/g.
in concentrations up to 19 mg/g.
kræves, at al ethoxyethanol i 1,5 g tusch fordamper momentant, hvilket ikke er realistisk med et damptryk på ca. 5 mm Hg.
all the ethoxyethanol in 1.5 g ink shall evaporate instantaneously, which is not realistic at a vapour pressure of approx. 5 mm Hg.
Koncentrationen af den fordelte ethoxyethanol vil maksimalt kunne nå 2,5 mg/m
The concentration of the spread ethoxyethanol will maximum be 2.5 mg/m
I de undersøgte produkter er der fundet en række sundhedsskadelige stoffer.
In the analysed products we have found a number of harmful substances.
For 11 af stofferne er opstillet eksponeringsscenarier og sundhedsvurderinger for børn og unge med udgangspunkt i, at to barnehåndflader bemales.
For 11 of these substances we have prepared exposure scenarios and health risk assessments based on scenario with two painted child palms.
Irriterende og sensibiliserende effekter
Irritant and sensitizing effects
R41 risiko for alvorlig øjenskade R43 sensibiliserende
R41 risk of serious eye damage R43 sensitizing
Carc3;R40 Mulighed for kræftfremkaldende effekt
Carc3;R40 Possible carcinogenic effect
Mut3;R68 mulighed for varig skade på helbred
Mut3;R68 Risk of permanent damage to health
Carc.cat.2;R45 kan fremkalde kræft
Carc.cat.2;R45 Carcinogenic
Er muligvis kræftfremkaldende ud fra data for N,Ndimethylanilin og anilin
Potential carcinogenic based on data for N,N-dimethylaniline and aniline
Muligvis kræftfremkaldende ud fra forsøg i rotter og mus
Potential carcinogenic based on animal tests
Rep.2;R61 kan skade barnet under graviditeten
Rep.2;R61 harmful to unborn child
Er muligvis kræftfremkaldende ud fra data for o-anisidin og N-methyl-panisidin
Potential carcinogenic based on data for oanisidine and Nmethyl-p-anisidine
Rep.cat.2:R60 Kan skade forplantningsevnen, samt R61 kan skade barnet under graviditeten
Rep.cat.2:R60 May be harmful to reproduction with R61 harmful to unborn child
R38 irriterer huden
R38 skin irritation
Der er ydermere fundet andre stoffer med effekter, hvor der ikke er foretaget sundhedsvurdering.
There are also other substances in the products that have health effects, but a health assessment is not made.
Af de undersøgte produkter er der i alt fundet:
In the products investigated in the report there has been found:
• 7 stoffer med mulig eller bevist kræftfremkaldende effekt
• 7 substances with potential or proven carcinogenic effect
I Tabel 4.3 er vist en resultaterne af vurderingen af toksisk effekt af stofferne.
Table 4.3 shows the results of the assessment of their toxic effect.
Tabel 4.3 Toksiske effekter af udvalgte stoffer i produkterne for børn og unge Stof
Table 4.3 Toxic effects of selected substances Substance
Max. optagelse mg pr. kg kropsvægt
Max.Intake mg per kg b.w.
NOAEL mg/kg kropsvægt pr. dag
NOAEL mg/kg b.w. per day
Ingen risiko for toksiske effekter ved oral optag, mindre risiko ved hudoptag, mulig risiko for kræftfremkaldende effekter hvis data fra rotter kan overføres til mennesker.
No risk of toxic effects by skin absorption, minor risk by oral intake, potential risk of carcinogenic effects
Ingen risiko, dog er kræftfremkaldende effekter af stoffet ikke tilstrækkeligt undersøgt
No risk, but carcinogenic effects not thoroughly investigated
Tabel 4.4 Toksikologiske effekter for produkter Produkt nr.
Table 4.4 Toxilogical effects Product no.
Toksisk effekt ud fra sundhedsvurdering
Toxic effect based on health assessment
Der er således fundet 10 produkter med tuschpenne, 5 produkter med glimmerlim og 4 produkter med akrylmaling og en gelpen med sundhedsskadelige effekter.
Hazardous substances were found in 10 marker pen products, 5 glitter glue products, 4 acrylic paint products and in one gel pen.
I de undersøgte dufttuscher er fundet de allergene stoffer d-limonen, benzylalkohol og citral i koncentrationer på mellem 0,01 og 0,1 vægtprocent.
The analysed aroma pen contained the allergenic substances d-limonene, benzylalcohol and citral in concentration of between 0.01 and 0.1 weight percentage.
I følgende produkter er der ikke fundet CMR eller allergene stoffer:
Generally, the content of heavy metals in the analysed products is low.
Et estimat af maksimal fordampning af formaldehyd i et lille børneværelse viser, at formaldehydindholdet i 6 gram (ca. 6 ml) glimmerlim maksimalt kan bidrage med op til 25 % af den anbefalede maksimale indeklimakoncentration i et børneværelse på 3 * 3 * 2 m. Det må derfor anbefales ikke at lade arbejde med kreationer hvor der over kort tid bruges større mængder glimmerlim (flere tuber) i små lukkede børneværelser med dårlig luftskifte.
An estimate of maximum evaporation of formaldehyde in a small child's room shows that the formaldehyde content in 6 gram (ca. 6 ml) glitter glue can maximum contribute with up to 25 % of the recommended indoor climate concentration in a room of 3 * 3 * 2 m. It is therefore not recommended to work with large amounts of glitter (several tubes) in small rooms with inferior air circulation.
Indholdet af tungmetaller i produkterne er generelt lavt.
Generally, the content of heavy metals in the analysed products is low.
Således er indholdet af bly ikke konstateret over 21 ppm og der er ikke fundet cadmium.
Thus no contents of lead over 21 ppm and no cadmium was found.
Resten af tungmetallerne stammer formodentlig fra farver, fra ”glimmerstykker” i glimmerlim eller spormængder af stofferne i farvestoffer.
The remaining heavy metals probably come from colorants, glitter particles or trace amounts of the substances in the colourants.
I vurderingen af stoffer blev identificeret en række miljøskadelige stoffer.
In the assessment of substances a number of environmentally hazardous substances were identified.
Anilin, CAS-nr.
Aniline, CAS-no.
62-53-3 er miljøfareklassificeret som N;R50.
62-53-3 has environmental classification N;R50.
I Tabel 5.1 er vist økotoksikologiske data for anilin for fisk, dafnier og alger.
Table 5.1 shows ecotoxilogical data for aniline in fish, daphnia and algae.
Tabel 5.1 økotoksikologiske data for anilin Organisme
Table 5.1 Ecotoxilogical data for aniline Organism
LC50, 96 timer = 10,6 mg/l
LC50, 96 hours = 10,6 mg/l
Daphnier (Daphnia pulex)
Daphnia (Daphnia pulex)
EC50, 48 timer = 0,1 mg/l
EC50, 48 hours = 0,1 mg/l
Daphnier (Daphnia cucullata) EC50, 48 timer = 0,68 mg/l
Daphnia (Daphnia cucullata) EC50, 48 hours = 0,68 mg/l
Daphnier (Daphnia magna)
Daphnia (Daphnia magna)
Alge (Selenastrum capricornutum)
Algae (Selenastrum capricornutum)
Anilin har en oktanol-vand fordelingskoefficient på log Kow = 0,9.
Aniline has an octanol-water distribution coefficient of log Kow = 0,9.
Stoffet har en Henrys lov konstant på 2.02 *10
Henry's law constant for aniline is 2.02 *10
Bioakkumuleringen er bestemt til BCF=2,6 (Eu risk assessment, 2004).
Bioaccumulation is determined to BCF=2.6 (EU risk assessment, 2004).
Forsøg med bionedbrydelighed viser en let nedbrydelighed under aerobe forhold.
Biodegradability tests establish easy degradability of the substance under aerobic conditions.
Stoffet er ikke bionedbrydeligt under anaerobe forhold.
The substance is not biodegradable under aerobic conditions.
En beregning med SIMPLETREAT giver mere end 87 % fjernelse i spildevandsanlæg.
A SIMPLETREAT calculation gives more than 87 % removal in a waste water plant.
Resultatet ses af appendix II, del 2 af (TGD, 2003).
The results can be seen from Appendix II, part 2 in (TGD, 2003).
Af Tabel 5.1 ses, at stoffet er mest giftigt for dafnier med en giftighed op til en faktor 10 over kravene for mærkning med R50.
Table 5.1 indicates that the substance is most toxic for daphnia with a toxicity factor of 10 over the requirements for marking with the R-phrase R50.
I er EU's risikovurdering for anilin er angivet data for forsøg hvor NOEC er bestemt for dafnier.
An EU risk assessment for aniline includes test data where NOEC has been determined for daphnia.
Middelværdien af 3 forsøg med bestemmelse af effekt over 21 dage er anvendt til at beregne NOEC =15µg/l.
The mean value of 3 tests with effect determination over 21 days was used for calculating NOEC =15µg/l.
Den estimerede nuleffekt koncentration for organismer der lever i vand PNECvand er beregnet til 1,5 µg/l ved at benytte en vurderingsfaktor på 10 (Eu risk assessment, 2004).
The estimated zero effect concentration for aquatic organisms PNECvand is calculated to 1.5 µg/l using an evaluation factor of 10 (EU risk assessment, 2004).
5.2 p-Chloranilin p-Chloranilin, CAS-nr.
5.2 p-chloroaniline p-chloroaniline, CAS-no.
106-47-8 er miljøfareklassificeret med N;R50-53.
106-47-8 is classified with N;R50-53.
I Tabel 5.2 er vist økotoksikologiske data for anilin for fisk, dafnier og alger.
Table 5.2 shows the ecotoxilogical data for fish, daphnia and algae.
Tabel 5.2 økotoksikologiske data for p-chloranilin Organisme
Table 5.2 Ecotoxilogical data for p-chloroaniline Organism
Fisk (Bluegill Lepomis macrochirus)
Fish (Bluegill Lepomis macrochirus)
Dafnier (Daphnia magna)
Dafphnia (Daphnia magna)
Alger (Scenedesmus subspicatus)
Algae (Scenedesmus subspicatus)
3/mol ved 25 ˚C (US EPA, 2004).
3/mol at 25 ˚C (US EPA, 2004).
Bioakkumulering i fisk ligger i området en faktor 4-20, mens opkoncentrering i alger kan være langt højere.
Bioaccumulation of fish has a factor in the area of 4-20, whereas the concentration in algae may be considerably higher.
Dette kan dog skyldes absorption til overflader (CICAD, 2003).
This may be due to the absorption to surfaces (CICAD, 2003).
Data for bionedbrydelighed viser, at stoffet ikke er let nedbrydeligt under aerobe forhold.
Data for biodegradability indicate that the substance is not easy degradable under aerobic conditions.
3 forskellige aerobe bionedbrydelighedstest over 28 dage af ”closed bottle” typen viser således en nedbrydelighed fra 0-7 %.
3 different aerobic biodegradability tests over 28 days of the ”closed bottle” type demonstrated a degradation from 0-7 %.
Stoffet viser en lille bionedbrydelighed under anaerobe forhold.
The substance indicates a low degree of biodegradability under anaerobic conditions.
Ved et opslag i TGDs SIMPLETREAT model under ”inherent biodegradability”, appendix II, del 2 af (TGD, 2003) angiver modellen, at ca. 41 % forventes fjernet i spildevandsanlæg.
The TGDs SIMPLETREAT model under ”inherent biodegradability”, appendix II, part 2 of (TGD, 2003) states that approx. 41 % is expected to be removed in the sewage plant.
p-Chloranilin nedbrydes af lys med bølgelængder over 290 nm med en halveringstid på 7 timer og nedbrydes således hurtigt ved fotolyse i overfladevand..
p-chloroaniline is degraded by light with wave lengths over 290 nm with a half-life period of 7 hours and is thus quickly degraded by photolysis in surface water.
I atmosfæren nedbrydes stoffet af hydroxylradikaler med en estimeret halveringstid i troposfæren på ca. 4 timer (CICAD, 2003).
In the atmosphere the substance is degraded by hydroxyl radicals with an estimated half-life period in the troposphere of approx. 4 hours (CICAD, 2003).
Af tabellen ses, at stoffet er mest giftigt for dafnier med en giftighed op til en faktor 3 over kravene for mærkning med R50.
The table indicates that the substance is most toxic for daphnia with a toxicity of up to a factor 3 over the requirements for R50 classification.
I (CICAD, 2003) er angivet data for forsøg hvor NOEC er bestemt i et 21 dages forsøg for dafnier til NOEC=0,01 mg/l. Dette er i samme størrelsesorden som for anilin.
In (CICAD, 2003) data was found where NOEC in a 21-day test with daphnia is determined to NOEC=0.01 mg/l. This is approximately, the same as for aniline.
Ud fra NOEC kan nuleffekt koncentrationen for organismer der lever i vand PNECvand estimeres til 1,0 µg/l ved at benytte en vurderingsfaktor på 10.
From the NOEC the zero effect concentration for aquatic organisms PNECwater be estimated to 1.0 µg/l by using an evaluation factor of 10.
Af stoffer, som er kvantificeret er fundet 5 stoffer, som er miljøskadelige.
Of the substances quantified we found 5 which were harmful to the environment.
Tabel 5.3 Miljøskadelige stoffer i produkter Stof
Table 5.3 Environmentally harmful substances in the products Substance
Koncentration mg/g
Concentration mg/g
For stoffer mærket med R53 er den samlede mængde, som tilledes spildevandsanlæg estimeret i Tabel 5.4.
The amounts of substances with an R53 classification fed to the sewage plant are listed in Table 5.4.
Det antages, at stofferne benyttes af alle danske børn fra alderen 3 til 13 med de eksponeringsscenarier, som er opstillet for stofferne under sundhedsvurderingen.
It is expected that the substances are used by all Danish children of 3-13 years with the exposure scenarios described in the health assessment.
Det antages, at al stof afvaskes inden absorption til huden er sket, og at stofferne herefter ledes med spildevand til renseanlæg.
It is assumed that the substances are washed off the skin before absorption and that they are subsequently flushed with the waste water to the sewage plant.
Tabel 5.4 Estimat af mængder af miljøskadelige stoffer i produkterne tilført danske renseanlæg
Table 5.4 Estimate of environmentally harmful substances supplied to the Danish sewage plant from the products analysed Substance
Stof, som afvaskes (mg/barn/dag)
Washed off substance (mg/child/day)
Stof ledt til renseanlæg, DK (g/dag)
Substance led to sewage plant, DK (g/day)
Samlet ledes således maksimalt 412 gram af stofferne til renseanlæg i Danmark.
Totally a maximum of 412 gram of the substances are led to sewage plants in Denmark.
Det dominerende stof er p-chloranilin med 348 gram og stoffet er samtidig det mest giftige af stofferne.
The most dominant substance is p-chloroaniline with 348 g and it is also the most toxic of the substances.
Stoffet benyttes derfor som et ”worst case”-stof til at vurdere den mulige miljøbelastning.
Therefore it is used as ”worst case” in order to evaluate the possible environmental impact.
Det er ud fra data for bionedbrydelighed antaget, at p-chloranilin ikke nedbrydes nævneværdigt i renseanlæg.
From data on biodegradability it is assumed that p-chloroaniline is not degraded significantly in the sewage plant.
Der er for p-chloranilin estimeret en begrænset nedbrydning i spildevandsbehandlingsanlæg på 41 % ud fra SIMPLETREAT.
Based on the SIMPLETREAT method a limited degradation in sewage treatment plants of 41 % has been estimated for p-chloroaniline.
I Tabel 5.5 er beregnet forholdet mellem den maksimale udledte koncentration i vandmiljøet PEClokal,vand og nul-effekt værdien PNEC.
Table 5.5 calculates the ratio between the maximum discharged concentration in the water environment PEClocal,water and the zero-effect value PNEC.
Der er benyttet følgende beregningsformler:
The following calculation formula has been used:
Koncentration i udledt spildevand Ceff::
The concentration in the discharged waste water Ceff::
Ceff = Cind *(1-f), hvor f er nedbrydningsgraden i renseanlæg og Cind er koncentrationen i det tilførte spildevand.
Ceff = Cind *(1-f), where f is the degradation degree in sewage plants and Cind is concentration in the supplied waste water.
Clokal, vand= Ceff /Fortyndingsfaktor.
Clocal, water= Ceff /Dilution factor.
Fortyndingsfaktoren er sat til 10 som angivet i TGD (Technical Guidance Document, 2003).
The dilution factor has been set at 10 as specified in TGD (Technical Guidance document, 2003).
Der er ikke taget hensyn til eventuel absorbtion af p-chloranilin til opløst stof i vandet.
Any absorption of pchloroaniline in dissolved form in water has not been taken into account.
Koncentrationen af p-chloranilin fra andre kilder PEC reg,vand er sat til 0 hvorfor
The concentration of p-chloroaniline from other sources PEC reg,vand has been fixed to 0 thus
Tabel 5.5 Beregnet effekt på vandmiljøet Parameter
Table 5.5 Calculated effect on water environment Parameter
Mængde tilført renseanlæg g
Amount supplied to sewage plant g
Koncentration i tilført spildevand (ug/l)
Concentration in supplied waste water (ug/l)
Antaget nedbrydelighed i renseanlæg % 41
Assumed degradation in waste water plant % 41
Det ses, at koncentrationen af PEClokal,vand/PNEC << 1 hvorfor der ikke forventes nogen effekt fra p-chloranilin på vandmiljøet.
As can be seen the concentration of PEClocal,water/PNEC << 1 and therefore pchloroaniline is not expected to have any impact on the water environment.
Det skal her bemærkes, at det anvendte stof p-chloroanlin kun indgår i et mindre antal af produkterne med akrylmaling hvorfor den gennemsnitlige effekt forventes endnu mindre.
In this connection it shall be noted that p-chloroaniline is found only in a small number of the acrylic paint products, so the average effect is expected to be even lower.
Da p-chloranilin er et repræsentativt stof for de undersøgte produkter med hensyn til koncentration af stoffet og giftighed, vurderes samlet, at mængden af miljøskadelige stoffer, som udledes til det vandmiljøet fra de undersøgte produktgrupper er uden betydning.
As p-chloroaniline is a representative for the analysed products regarding concentration of substance and toxicity, it is assessed that the amount of environmental harmful substances in the analysed products being flushed into the waters will have no influence on the environment.
HSDB Hazardous Substance Data Bank
HDSB Hazardous Substance Data Bank
Dødelig koncentration 50 procent
Lethal concentration 50 percent
Dødelig dosis 50 procent
Lethal dose 50 percent
LOAEL Lav skadelig virkning
LOAEL Lowest observed adverse effect level
Mutagen, skadelig for arveanlæg
Negative mutagenic effect
NOEC 0-effekt niveau
NOEC 0- effect level
PNEC Estimeret 0-effekt koncentration
PNEC Estimated 0-effect concentration
At-vejledning, Stoffer og materialer C.O.1.
At-vejledning, Indholdsstoffer og materialer C.O.1.
Assessment Document 48: nternational Programme on Chemical
Assessment Document 48: International Programme on Chemical
Bekendtgørelse nr. 923 af 28. september 2005.
Statutory Order No. no. 923 af 28. september 2005.
Typisk for otteradet ulvefod er, at der på forekomststederne, grundet vegetativ formering, ofte findes nogle få individer nær hinanden.
Two projects have looked at possible consumer and environmental risks and the main conclusions are presented in these reports:
Selvbrunerprodukter indeholdende dihydroxyacetone (DHA) som farvende stof har eksisteret i mange år.
Dihydroxyacetone (DHA) containing self-tanning products has existed for many years.
Hold munden lukket og beskyt læberne med læbepomade under behandlingen.
Manual turbine spray technique: The operator sprays the customer manually using a handheld spray pistol.
Dihydroxyacetone (DHA) containing self-tanning products has existed for many years.
All exposure assessments are based on realistic worst-case calculations.
The National Environmental Research Institute (NERI) was responsible for the monitoring programmes, and DTC conducted customer exposure assessments in connection with three booth techniques:
Furthermore, exposure of the eyes and mucous membranes to DHA and the self-tanning preparations constitute a greater quantitative exposure than inhalation.
Continuous weekly treatment over a long time can not be recommended as long as there is insufficient knowledge of the effects of DHA.
Continuous weekly treatment over a long time cannot be recommended as long as there is insufficient knowledge of the effects of DHA.
The genreral recommendations should be followed and sun tan lotion should be used, when exposed to the sun.
The general recommendations should be followed and sun tan lotion should be used, when exposed to the sun.
Selvbrunerprodukter har eksisteret i mange år som cremer, der smøres på huden.
Self-tanning products have existed for many years as lotions to be rubbed onto the skin.
I den senere tid er der sket en udvikling, idet der siden 1999 (1) har været kabiner på markedet, hvor selvbrunerprodukter mere eller mindre automatisk bliver sprayet på kundens krop.
In recent years a new development has taken place in that since 1999 (1) there have been booths on the market in which self-tanning products are more or less automatically sprayed onto the customer's body.
Formålet med kabinerne er at få en jævnere fordeling af selvbrunerproduktet end ved manuel påføring.
The purpose of the booths is to achieve a more even covering of the self-tanning product than through manual application.
Den tid som kunden typisk opholder sig i kabiner med automatisk påføring varierer mellem 6 og 60 sekunder.
The customer is usually in the booth for automatic application for between 6 and 60 seconds.
For de kabiner, hvor der sker en manuel turbinespray, skal man regne med længere opholdstid i kabinen, typisk 2-3 minutter.
Time spent in booths for manual application using a turbine spray is longer, typically from 2-3 minutes.
Der findes mange forskellige selvbrunerprodukter på markedet.
There are many different types of self-tanning product on the market.