natgillin/translations-raw huggingface dataset:
Akut toksicitet for rotter ved indtagelse er bestemt til mindst 2400 mg/kg (LD50). 
Acute toxicity to rats by ingestion has been determined to at least 2400 mg/kg (LD50).
Akut toksicitet: Akut oral, rotte, hun LD50 
Acute toxicity: Acute oral rat, female LD50
Akut oral, rotte, han LD50 
Acute oral rat, male LD50
Af undersøgelser for gentagen eksponering er der kun fundet resultater fra et oral rottestudie, hvor LOAEL var 4060 mg/kg/14 dage med kontinuerlig eksponering baseret på skadelige effekter i blodbilledet (Arch. Toxicol. 
When examining repeated dose exposure studies, only results from an oral rat study has been found, where LOAEL was 4060 mg/kg/14 days with continuous exposure based on harmful effects in the blood parameter (Arch. Toxicol.
Baseret på erfaringer med glycol ethere anbefaler NIOSH at reducere eksponeringen til lavest mulige koncentration og at undgå kontakt med huden (NIOSH 1988, HSDB). 
Based on experiences with glycol ethers NIOSH recommends reducing exposure to lowest feasible concentration and preventing contact with the skin (NIOSH 1988, HSDB)
bestemt for rotter. 
butyl ether and
De dermale absorptionsrater blev estimeret til 1,58 (diethylene glycol butyl acetate derivater, for hanner), 1,28 (diethylene glycol butyl acetate derivater, for hunner), 0,73 (diethylene glycol butyl ether, for hanner), 1,46 (diethyl glycol butyl ether, for hunner), udtrykt som mg/cm3/time (Boatman et al. 1993). 
The dermal absorption rates were estimated to be 1.58 (diethylene glycol butyl acetate derivative, male), 1.28 (diethylene glycol butyl acetate derivative, female), 0.73 (diethylene glycol butyl ether, male), and 1.46 (diethyl glycol butyl ether, female), expressed as mg/cm3/hour (Boatman RJ et al. 1993).
Ud fra dette er mængden af optaget stof beregnet i det følgende. 
Based on this, the amount of absorbed substance has been calculated below.
2-Butoxyethyl acetat er således påvist i 2 af produkterne i mængder over detektionsgrænsen på 0,15 µg/tandbørste. 
2-Butoxy-ethyl acetate has thus been detected in 2 of the products in amounts above the detection limit of 0.15 µg/toothbrush.
Glycol ether acetater har de samme systematiske toksikologiske effekter som deres tilsvarende glycol ethere. 
Glycol ether acetates have the same systematic toxicological effects as their corresponding glycol ethers.
Det er derfor rimeligt at antage, at deres toksicitet er ækvivalent på molær basis ifølge Jensen et al. (1999). 
It is therefore reasonably to assume that their toxicity is equivalent on molar basis according to Jensen et al. (1999).
Baseret på de få tilgængelige oplysninger synes den anvendte værdi for en tolerabel koncentration at være begrundet tilstrækkeligt til dette formål. 
Based on the few available data, the used value for tolerable dose is considered sufficiently supported for this purpose.
Med en sikkerhedsmargin på næsten (29/0,0038=) 8000 anses sikkerhedsafstanden for tilstrækkelig til, at stoffet vurderes ikke at ville indebære nogen væsentlig sundhedsmæssig risiko. 
With a safety margin of almost (29/0.0038=) 8000 the margin of safety should be sufficient to assess the substance not to be a health risk.
2-Butoxyethyl acetat indebærer ingen sundhedsmæssig risiko ved indtagelse i de mængder, der er konstateret ved analyse af de udvalgte tandbørster. 
2-Butoxy-ethyl acetate implies no health risks to the consumer by oral intake at the concentrations measured in the selected toothbrushes.
1-Butoxy-2-propanol anvendes som opløsningsmiddel for trykfarver, maling og harpikser. 
1-Butoxy-2-propanol is used as a solvent for printing inks, paint and resins.
5131-66-8 (a-isomer) 15821-83-7 (b-isomer) 63716-40-5 (Blanding/mixture) 29387-86-8 (Blanding/mixture) 
5131-66-8 (a-isomer) 15821-83-7 (b-isomer) 63716-40-5 (Mixture) 29387-86-8 (Mixture)
Stoffets smeltepunkt er skønnet til -22ºC. 
The melting point of the substances is estimated at -22°C.
1-Butoxy-2-propanol CAS 5131-66-8 er klassificeret i Listen over farlige stoffer (Miljøministeriet 2002): 
1-Butoxy-2-propanol, CAS 5131-66-8, is classified in the List of Dangerous Substances (Miljøministeriet 2002):
Det bemærkes, at b-isomeren, CAS nr. 15821-83-7, ikke er klassificeret. 
It should be noted that the b-isomer, CAS no. 15821-83-7, is not classified.
Den akutte toksicitet af 1-butoxy-2-propanol er lav. 
The acute toxicity of 1-butoxy-2-propanol (PGBE) is low.
LD50 værdierne for oral rotte ligger mellem 1900 og 5200 mg/kg (Jensen et al. 1999). 
The LD50 values for oral rat are between 1900 and 5200 mg/kg (Jensen et al. 1999).
1-Butoxy-2-propanol er øjenirriterende og kan beskadige øjnene, men er kun mildt irriterende for huden. 
1-Butoxy-2-propanol is eye irritating and somewhat injurious to the eyes, but only mildly irritating to the skin.
Der blev ikke fundet sensibilisering hos marsvin (Jensen et al. 1999). 
No sensitisation in guinea pigs has been found (Jensen et al 1999).
I reproduktionsstudier (oral, dermal eller eksponering ved injektion) på mus, rotter og kaniner blev der ikke fundet effekter på moderdyret eller fostrene (Jensen et al. 1999). 
In reproduction studies (oral, dermal or injection studies) on mice, rats and rabbits there has been found no effects on maternal toxicity or on foetuses (Jensen et al. 1999).
Men i mangel på data er 100% optagelse anvendt. 
However, in the absence of data, 100% absorption has been used.
Med udgangspunkt i kronisk NOEL på 350 mg/kg lgv/dag og en usikkerhedsfaktor på 1000 beregnes det tolerable effektniveau til 0,35 mg/kg lgv/dag. 
Based on chronic NOEL of 350 mg/kg bw/day and an uncertain factor of 1000, the tolerable effect level is calculated at 0.35 mg/kg bw/day.
Forholdet mellem den estimerede eksponering er (350/0,00024 =) > 1x10 
tween the estimated exposure is (350/0.00024=) >1´10
6, hvorfor eksponeringen for 1-butoxy-2-propanol vurderes ikke at ville indebære nogen sundhedsmæssig risiko. 
6. Therefore, the exposure to 1-butoxy-2-propanol is assessed not to involve any health risk.
1-Butoxy-2-propanol indebærer ingen sundhedsmæssig risiko ved indtagelse i de mængder, der er konstateret ved analyse af de udvalgte tandbørster. 
1-Butoxy-2-propanol implies no health risks to the consumer by oral intake at the concentrations measured in the selected toothbrushes.
Benzylbutylphthalat anvendes som plastblødgører i polyvinyl chlorid, polyvinyl acetat, gummi, cellulose plastik og polyurethan. 
Benzyl butyl phthalate is used as a plasticiser for polyvinyl chloride, polyvinyl acetate, rubbers, cellulose plastics and polyurethane.
Slutprodukterne omfatter PVC gulvbelægninger og vægbeklædninger, PVC skum, film, forseglinger og limsystemer baseret på polyurethan eller polysulfid, PVA baserede lime og bindemidler til maling. 
End applications include PVC floorings and wall coverings, PVC foams, films, sealing and adhesive systems based on polyurethane or polysulphide, PVA based adhesives and paint binders.
Stoffets smeltepunkt er -35ºC. 
The melting point of the substance is -35°C.
Kogepunktet er 370ºC ved 1,01 kPa (KirkOthmer 1982). 
The boiling point is 370°C at 1.01 kPa (Kirk-Othmer 1982).
Fordelingskoefficienten log Kow er fundet i litteraturen at variere mellem 3,5 og 5,8. 
The partitioning coefficient log Kow has been found in literature to vary between 3.5 and 5.8.
De fundne eksperimentelle værdier ligger omkring 4,7 til 4,9 (f.eks. 4,91 (Hansch et al. 1995)). 
The experimental values are found between approx. 4.7 to 4.9 (e.g. 4.91 (Hansch et al. 1995)).
Klassifikation Benzylbutylphthalat er ikke klassificeret (Miljøministeriet 2002). 
Classification Benzyl butyl phthalate is not classified (Miljøministeriet 2002).
T;R61 (Repr. cat. 
T;R61 (Rep. cat.
Kan skade barnet under graviditeten Xn;R62 (Repr.cat.3) Sundhedsskadelig. 
May cause harm to the unborn child Xn;R 62 (Rep.cat.3) Harmful.
Mulighed for skade på forplantningsevnen N;R50/53 
Possible risk of impaired fertility N;R50/53
Meget giftigt for organismer, der lever i vand; kan forårsage uønskede langtidsvirkninger i vandmiljøet 
Very toxic to aquatic organisms, may cause long-term adverse effects in the aquatic environment
Xn;R62 (Repr.cat 3) er baseret på tegn på effekter på testikler (atrofi af testikler, reduceret sædcelle produktion), samt reducerede niveauer i produktionen af testosteron og folikkelstimulerende hormon (FSH), hvor der ikke er fundet effekter i andre organer. 
Xn;R62 (Rep.cat.3) is based on signs of testicular toxicity (atrophy of the testes and decrease in epididymal spermatozoa concentration), and decreased testosterone and follicle stimulating hormone (FSH) levels are reported in the absence of effects in other organs.
Det konkluderes derfor, at benzylbutylphthalat muligvis kan påvirke fertiliteten (ECB 2002). 
It is therefore concluded that benzyl butyl phthalate may affect fertility (ECB 2002).
6.2.4.1 Effekter på sundhed 
6.2.4.1 Effect on health
Benzylbutylphthalat er under vurdering i EUs risikovurderingsprogram for eksisterende stoffer. 
Benzyl butyl phthalate is being evaluated under EU's risk assessment programme for existing substances.
Vurderingen er endnu ikke færdig, men et næsten færdigt udkast fra februar 2002 foreligger (ECB 2002). 
The evaluation is not yet finalised but an almost final draft from February 2002 is available (ECB 2002).
De fleste oplysninger er taget derfra. 
Most information is recovered from the draft.
Benzylbutylphthalat har en relativ lav akut toksicitet: 
Benzyl butyl phthalate possesses a relatively low degree of acute toxicity:
Akut oral, mus (hunhan) 
Acute oral mouse (femalemale)
Benzylbutylphthalat er ikke hudirriterende, eftersom der ikke blev fundet tegn på irritation eller sensibilisering hos 200 frivillige forsøgspersoner efter 15 dages daglige eksponeringer med benzylbutylphthalat. 
Benzyl butyl phthalate does not irritate the skin since no promaty irritation or sensitisation reactions were observed in 200 human volunteers after 15 daily applications of a subsequent challenge with benzyl butyl phthalate.
Efter oral eller inhalatorisk eksponering af benzylbutylphthalat til rotter var forøget levervægt (peroxisom proliferation) den mest følsomme effekt (Hammond et al. 1987). 
Following oral or inhalatory administration of benzyl butyl phthalate to rodents, peroxisome proliferation appeared to be the most sensitive effect (Hammond et al. 1987).
I et oral 90-dages studie på rotter med doseringerne 0, 171, 422 eller 1069 mg/kg lgv/dag for hunner og 0, 151, 381 eller 960 mg/kg lgv/dag for hanner, blev forøget levervægt set i alle doseringer hos hunner og ved 381 mg/kg lgv/dag og 960 mg/kg lgv/dag hos hanner. 
In an oral 90-day study in rats, at dose levels of 0, 171, 422 or 1069 mg/kg bw/day for females and 0, 151, 381 or 960 mg/kg bw/day for males, increased liver weights were seen at all dose levels in females and at 381 mg/kg bw/day and at 960 mg/kg bw/day in males.
Den forøgede levervægt var dog lille ved de laveste koncentrationer hos hunnerne. 
The increased liver weight in females was only slight at the two lower doses.
LOAEL for forøget levervægt og andre organændringer hos hunrotter var 171 mg/kg lgv/dag. 
The LOAEL for increased liver and cecal weights in females was 171 mg/kg bw/day.
NOAEL for forøget levervægt hos hanrotter var 151 mg/kg lgv/dag (Hammond et al., 1987). 
The NOAEL for increased liver weight in males was 151 mg/kg bw/day (Hammond et al., 1987).
I et oral 6 måneders studie blev der anvendt fødekoncentrationerne 0, 0,03, 0,09, 0,28, 0,83 og 2,5% benzylbutylphthalat, svarende til henholdsvis 0, 17, 51, 159, 470 og 1417 mg/kg lgv/dag. 
In an oral 6 month study on rats, food concentrations of 0, 0.03, 0.09, 0.28, 0.83 and 2.5% benzyl butyl phthalate were applied, corresponding to 0, 17, 51, 159, 470 and 1417 mg/kg bw/day, respectively.
Der blev observeret en relativ vægtforøgelse af lever og hjerne. 
A relative increase in weight of liver and brain was observed.
Studiet viste en LOAEL på 8300 ppm (470 mg/kg/dag) og en NOAEL på 2800 ppm i føden (svarende til 159 mg/kg lgv/dag) (NTP studie refereret i IRIS 2003). 
The study showed a LOAEL of 8300 ppm (470 mg/kg bw/day) and a NOAEL of 2800 ppm in the food (corresponding to 159 mg/kg bw/day) (NTP study referred in IRIS 2003).
NOAEL for effekter på udviklingen hos ungerne blev fundet til 50 mg/kg lgv/dag baseret på et dosisafhængigt fald i effekter på udviklingen af kønsorganer fra 250 mg/kg lgv/dag i både F1 og F2 generationen (Tyl et al., 2001). 
The NOAEL for effects on the development of the young was 50 mg/kg bw/day based on a dose-dependent effect on the reproductive organs (decrease in absolute and adjusted anogenital distance (AGD)) from 250 mg/kg bw/day in both the F1 and the F2 generation (Tyl et al. 2001).
Med hensyn til kræftfremkaldende effekt kan der ikke drages entydige konklusioner fra de tilgængelige dyreforsøg. 
With regard to cancer-causing effect no unambiguous conclusions can be drawn from the available animal experiments.
IARC har anbragt stoffet i kategori 3, dvs. ikke klassificerbart med hensyn til carcinogenicitet overfor mennesker. 
IARC has put the substance in category 3, i.e. not classifiable as to its carcinogenicity to humans.
For benzylbutylphthalat er der fundet østrogenlignende effekter i reagensglasforsøg (NCM 1996). 
For benzyl butyl phthalate oestrogenic effects have been found in test tube experiments (NCM 1996).
Forslag til fælles regulering har været diskuteret i EU (MEM 1999). 
A proposal for common regulation has been discussed in the EU (MEM 1999).
TDI: en foreløbig TDI-værdi på 0,1 mg/kg lgv/dag foreligger (EC 1997 i Baaars et al. 2001). 
TDI: a temporary TDI of 0.1 mg/kg bw/day is found (EC 1997 in Baars et al. 2001).
Siden da er der udført yderligere studier på benzylbutylphthalat. 
Since then several studies have been performed with BBP.
EUs videnskabelig komité (CSTEE) anbefaler, at vejledende værdier for ekstraherbare mængder af individuelle phthalater fra legetøj inkorporerer en sikkerhedsmargin (margin of safety) på mindst 100 fra de respektive NOAEL værdier. 
The EU scientific committee CSTEE recommends that guideline values for extractable amounts of individual phthalates in toys be produced, incorporating a margin of safety of at least 100 from their respective NOAEL values.
I tabellen nedenfor er angivet TDI (tolerable daily intake) værdier beregnet med NOAEL/100. 
In the table below, TDI (tolerable daily intake) values have been calculated by dividing the NOAEL values by 100.
Nedenstående tabel er en oversigt på de mest anvendte stoffers kritiske effekter, 
The scientific committee CSTEE has several times evaluated the risk from the different phthalates.
Tabel 6.4 NOAEL og TDI værdier for phthalater i legetøj (CSTEE 1998b) 
Table 6.4 NOAEL and TDI values for phthalates in toys (CSTEE 1998b)
DINP Di-iso-nonylphthalat Forøget lever- og nyrevægt 
DINP Di-iso-nonylphthalate Increased liver and kidney weight
P Di-n-octylphthalat 
DNOP Di-n-octylphthalate
Mikroskopiske celleændringer på lever og skjoldbrukskirtel 
Microscopic cell changes in liver and thyroid gland
Skader på testiklerne DIDP Di-iso-decylphthalat Forøget levervægt BBP Benzylbutylphthalat 
DIDP Di-iso-decylphthalate Increased liver weight BBP Benzylbutylpthahlate Decreased spermatozoa
Nedsat vægt af afkom 
Reduced weight of progeny
a: Laveste koncentration med effekt b: En yderligere sikkerhedsfaktor på 5 er sat på grund af, at der ikke er fundet et nuleffektniveau 
a LOAEL value b An additional uncertainty factor of 5 has been used as no NOAEL was found
I Miljøministeriets handlingsplan for phthalater er der for benzylbutylphthalat baseret på nedsat sædcelleproduktion angivet en NOAEL på 20 mg/kg/dag og en TDI-værdi på 0,2 mg/kg lgv/dag (MEM 1999). 
In an action plan for phthalates by the Danish Ministry of the Environment, based on decreased spermatozoa production, a NOAEL of 20 mg/kg/day and a TDI-value of 0.2 mg/kg bw/day has been stated (MEM 1999).
En RfD-værdi på 0,2 mg/kg lgv/dag er fastsat af US-EPA baseret på et oral 6 måneders studie, som gav en relativ vægtforøgelse af lever og hjerne. 
A reference dose (RfD) of 0.2 mg/kg bw/day has been determined by USEPA based on an oral 6 month study, which gave a relative increase in weight of liver and brain.
I et in vivo studie på rotter blev det fundet, at ca. 5% benzylbutylphthalat blev absorberet pr. dag over huden (Elsisi et al. 1989). 
In an in vivo study of rats it was found that approx. 5% BBP was absorbed per day via the skin (Elsisi et al. 1989).
Optagelsen over hud var således lav (5%/dag), mens den var op til 74% ved oral indgift. 
The absorption via the skin was thus low (5%/day), while it was up to 74% by oral administration.
Da oral optag nok bedst simulerer slimhindeoptagelsen, er den anvendt. 
Oral absorption has been used because it probably simulates the mucous membrane absorption most accurately.
B-006 -: under detektionsgrænsen på 0,15 µg/tandbørste 
B-006 -: Below the detection limit of 0.15 µg/toothbrush
Da Miljøstyrelsen, CSTEE og US-EPA er enige om en TDI på 200 µg/kg lgv/dag, er denne anvendt i vurderingen. 
As the Danish EPA, CSTEE and the US-EPA agree upon a tolerable value (TDI) of 200 µg/kg bw/day, this has been used in the evaluation.
Af ovenstående ses, at ingen af de mængder, der indtages eller optages, vil medføre en dosis på over TDI (eller RfD)-værdien på 0,2 mg/kg, hvorfor dette vurderes ikke at ville indebære nogen sundhedsmæssig risiko. 
From the above it is observed that none of the amounts of benzyl butyl phthalate ingested or absorbed at toothbrushing will result in a dose above the TDI (or RfD)-value of 0.2 mg/kg bw/day, for which reason it is assessed not to involve any health risk.
Benzylbutylphthalat indebærer ingen sundhedsmæssig risiko ved indtagelse eller optagelse i de mængder, der er konstateret ved analyse af de udvalgte tandbørster. 
Benzyl butyl phthalate implies no health risks to the consumer by oral intake or inhalation at the concentrations measured in the selected toothbrushes.
Carvon er et naturligt plantestof. 
Carvone is a natural plant substance.
Carvon kan være produceret ud fra destillation af pebermynteolie, som kan indeholde 50-70% L-carvon (Kirk-Othmer 1983), eller syntetiseret fra D-limonene eller alfa-pinen (Budavari 1989). 
Carvone can be produced from distillation of spearmint oil, which contains 50-70% L-carvone (Kirk-Othmer 1983), or synthesised from D-limonene or alfa-pinene (Budavari 1989).
Carvon anvendes mest som duftstof i parfumer og sæber og som smagsstof til at fremhæve pebermyntesmag i f.eks. tandpasta. 
Carvone is mostly used as fragrant in perfumes and soaps and as flavouring in order to emphasise the peppermint taste in e.g. toothpaste.
L-carvon er ikke klassificeret under eget navn, men stoffet er en monoterpen. 
L-carvone is not classified under its own name, but the substance is a monoterpene.
Terpenerne kan komme fra anvendelsen af vegetabilske olier og harpikser (resiner) i trykfarverne som opløsningsmiddel. 
The terpenes might derive from the use of plant oils and resins as a solvent in the printing ink.
Terpenerne er generelt slimhindeirriterende. 
The terpenes are generally irritating to the mucous membrane.
Terpentin fra nåletræer er hudsensibiliserende. 
Turpentine from coniferous trees is skin sensitising.
Sensibiliseringen er dog ikke bekræftet for de enkelte terpener med undtagelse af 3-caren, CAS no. 13466-78-9 (ASS 2000). 
However, the sensitising has not been confirmed for the individual terpenes, except for 3-carene, CAS no. 13466-78-9 (ASS 2000).
Hvis carvon henregnes som enten mineralsk eller vegetabilsk terpentin (Miljøministeriet 2002), er klassifikationen: 
If carvone is considered as either mineral or vegetable turpentine (Miljøministeriet 2002), the classification is:
Carc2;R45 R10 Kan fremkalde kræft. 
Carc2;R45 R10 May cause cancer.
Brandfarlig Xn;R48/20-65 Farlig: Alvorlig sundhedsfare ved længere tids påvirkning ved indånding. 
Inflammable Xn;R48/20-65 Harmful: Danger of serious damage to health by prolonged exposure through inhalation.
- Kan give lungeskade ved indtagelse 
- May cause lung damage if swallowed
Xi;R36/38 R43 Irriterer øjnene og huden. 
Xi;R36/38 R43 Irritant, Irritating to eyes and skin.
6.2.5.1 Effekter på sundhed Carvon er en monoterpen (terpenoid keton). 
6.2.5.1 Effects on health Carvone is a monoterpene (terpenoid ketone).
L-Carvons sensibiliserende virkning anses normalt for lav, men har af og til forårsaget kontaktallergi hos brugere af pebermynte tandpasta og tyggegummi. 
The sensitising potential of L- carvone is normally considered low, but it has occasionally caused contact allergy in users of spearmint toothpaste and chewing gum.
I en lappetest (”patch-test”) undersøgelse af 541 patienter havde 15 (2,8%) positive og 12 tvivlsomme positive reaktioner over for l-carvon. 
In a ”patch-test” examination of 541 patients, 15 (2.8%) had positive and 12 had doubtful positive reactions towards L-carvone.
I en gentestning med l-carvon i samme eller lavere koncentrationer havde kun 2 ud af 8 patienter positive reaktioner (Paulsen 1993: HSDB). 
In a repeated test with L-carvone in the same or lower concentrations only 2 out of 8 patients had positive reactions (Paulsen 1993: HSDB).
L-carvon er også et oxidationsprodukt af d-limonene, hvis oxidationsprodukter er erkendt som hudsensibiliserende (AT 2002). 
L-carvone is also an oxidation product of d-limonene, whose oxidation products are known as skin sensitising (AT 2002).
Akut oral, marsvin LD50 
Acute oral guinea pig LD50
Der blev ikke noteret skadelige effekter på kropsvægtsforøgelse eller væsentlige organer og væv inklusiv testikler (Hagan et al. 1967). 
No adverse effects were noted on body-weight gain or main organs and tissues, including testes (Hagan et al. 1967).
Dosisniveauet, der ikke medførte toksiske effekter, var således 0,25% i foderet (= 2500 ppm) svarende til 125 mg/kg lgv/dag. 
Level causing no toxicological effect was thus 0.25% (= 2500 ppm) in the diet, equivalent to 125 mg/kg bw/day.
Det daglige indtag af carvone (begge isomere) pr. capita er anslået til 2,8 mg/person (JECFA 1999). 
The daily intake of carvone (both isomers) per capita is estimated at 2.8 mg/person (JECFA 1999).
Regneeksempel med udgangspunkt i den højest målte migration på 0,65 µg/tandbørste: 
Example of calculation based on the highest migration measured to 0.65 µg/toothbrush:
Af ovenstående ses, at ingen af de mængder, der indtages eller optages ved indånding, vil medføre en dosis på over den midlertidige ADI på 1,25 mg/kg lgv/dag, hvorfor dette vurderes ikke at ville indebære nogen sundhedsmæssig risiko. 
From the above it is seen that none of the amounts ingested or absorbed at toothbrushing will result in a dose above the temporary ADI of 1.25 mg/kg bw/day, for which reason it is assessed not to involve any health risk.
Carvon indebærer ingen sundhedsmæssig risiko ved indtagelse i de mængder, der er konstateret ved analyse af de udvalgte tandbørster. 
Carvone implies no health risks to the consumer by oral intake at the concentrations measured in the selected toothbrushes.
N,N-Dimethyacetamid anvendes mest som opløsningsmiddel (solvent) i industrielle anvendelser. 
N,N-Dimethylacetamide is mostly used as a solvent in industrial applications.
N,N-Dimethylacetamid bruges f.eks. som solvent for plastik, harpiks (resins and gums), som katalysator i kemiske processer og i malingfjerner. 
N,N-Dimethylacetamid is e.g. used as a solvent for plastics, resins and gums, as catalyst in chemical processes, and paint remover.
N,N-Dimethylacetamid kan opløse polyacrylonitril, polyvinylchlorid, polyamid og polyimid. 
Polyacrylonitrile, polyvinylchloride, polyamide and polyimide can be dissolved by N,Ndimethylacetamide.
Dimethylacetamid anvendes desuden i produktionen af film og fibre. 
N,N-Dimethylacetamide is furthermore used in the production of films and fibres.
For eksempel angiver BASF, at dimethylacetamid anvendes i produktionen af polyacrylonitril fibre, film og overfladedækkende stoffer som lakker (BASF 2001). 
For instance, BASF informs that N,N-dimethylacetamide is used in the production of polyacrylonitril fibres, films and coatings and for special lacquers (BASF 2001).
IUPAC navn N,N-dimethylacetamid 
IUPAC name N,N-Dimethylacetamide
dimethylacetamid acetdimethylamid dimethylamid acetat 
dimethylacetamide acetdimethylamide dimethylamide acetate