natgillin/translations-raw huggingface dataset:
Resultaterne kommenteres yderligere i kapitel 4 og 5. 
The results are subject to further comment in chapters 4 and 5.
I det følgende er foretaget en screening af de sundhedsmæssige effekter for de stoffer, der er fundet i analyserne. 
In the present chapter a screening is presented for the health effects of the substances, which have been detected in the test programme.
Screeningens mål er at udpege de stoffer, der kan indebære en potentiel sundhedsmæssig risiko for børn ved leg med produkterne. 
The object of the screening is to point out the substances that may cause a potential health risk for children when playing with the products.
Dernæst er alle stoffer gennemgået med hensyn til, om de er optaget på listen over farlige stoffer (bekendtgørelse nr.439, 2002) eller Miljøstyrelsens vejledende liste over farlige stoffer til selvklassificering. 
It has been checked whether the substances are included in the list on dangerous substances (the Danish statutory order no 439, 2002) or the guideline of self-classification of dangerous substances of the Danish EPA.
For de stoffer, der er fastsat grænseværdier i arbejdsmiljøet, er disse værdier ligeledes anvendt (At-vejledning C.0.1, 2002). 
As for the substances for which threshold limit values (TLV) in the working environment have been determined, the values have also been used (Atvejledning C.0.1, 2002).
De stoffer, for hvilke den højeste målte koncentration udgør mindre end 1 % af grænseværdien, og for hvilke der samtidig ikke er konstateret langtidseffekter, sorteres fra i første omgang. 
The substances for which the highest concentration constitutes less than 1 % of the TLV and for which no long-term effects have been detected sorted out at first.
For en række stoffer er der ikke fastsat en klassificering eller en grænseværdi. 
For a number of the substances no classification or no TLV has been determined.
I tabel 4.1 er visse stoffer markeret med "*". 
In table 4.1 these substances are registered with "*".
Dette indikerer at der ikke foreligger en grænseværdi for stoffet eller at stoffet ikke er klassificeret eller begge dele. 
It indicates that there is no TLV for substance or the substance is not classified or both the priors mentioned.
Screeningen af disse stoffer er gennemgået i afsnit 4.2. 
The screening of these substances is discussed in section 4.2.
Tabel 4.1 Oversigt over målte stoffer og deres koncentrationer efter tre timers ophold i klimakammer 
Table 4.1 Outline on the measured substances and their concentrations after three hours in the climatic chamber
Indhold målt i µg/m 
Concentration measured in µg/m
4.2 Screening af stoffer 
4.2 Screening of substances
Alle stoffer i tabel 4.1 er screenet. 
All the substances in table 4.1 have been screened.
I tabel 4.1 er anført klassificeringen for de stoffer, der er anført på listen over farlige stoffer. 
In table 4.1 the classification of the substances appearing on the list on dangerous substances is listed.
Endvidere er det kontrolleret, om der er fastsat en grænseværdi. 
Furthermore, it has been monitored whether a TLV has been determined.
Hvis der ikke har været fastsat både en grænseværdi og en klassificering for et stof, er der foretaget en screening med henblik på at finde supplerede oplysninger om stoffer, der strukturmæssigt ligner det aktuelle stof. 
If neither a TLV nor a classification of a substance have been determined a screening has been carried out in anticipation of finding supplementary data on substances that, in structure, are similar to the substance in question.
De stoffer, der er fundet supplerende oplysninger om, er i tabel 4.1 mærket med en "*" ud for nummeret. 
The substances, for which supplementary data have been retrieved, are marked with an "*" in table 4.1.
CAS-nr 4254-15-3 står for (S)-(+)-1,2-Propanediol. 
CAS-no 4254-15-3 represents (S)-(+)-1,2Propanediol.
Der findes ingen officiel klassificering for stoffet, og der er ikke angivet en grænseværdi for stoffet. 
Official classification of the substance does not exist nor has the substance a TLV.
Stoffet er en C8-alkohol. 
The substance is a C8-alcohol.
I Gosselin et al., 1976, er det anført, at 2-ethylhexanol ligner butylalkoholer med hensyn til giftighed. 
In Gosselin et al., 1976, it is stated that 2-ethylhexanol is similar to butyl alcohol regarding toxicity.
Som en konservativ indledende vurdering anvendes derfor klassificeringen for butanol (R10 Xn;R22 Xi;R37/38-41 R67). 
As a conservative preliminary assessment of the substance the following classification is therefore used for butanol (R10 Xn;R22 Xi;R37/38-41 R67).
4.2.1.4 3-Caren og α -pinen 
4.2.1.4 3-Caren and α -pinene
Stofferne betegnes terpener. 
The substances are described as terpenes.
Carener og pinener minder i deres struktur til en vis grad om vegetabilsk terpentin. 
Carene and pinene resembles in their structure to a certain extent to turpentine.
Det må derfor antages at carener og pinener er sundhedsskadelige, allergifremkaldende og miljøfarlige. 
It is therefore assumed that carene and pinene are hazardous to the health, may cause allergic reactions and are hazardous to the environment.
Data for vegetabilsk terpentin anvendes i det følgende. 
Data on turpentine are used in the following assessment.
Stoffet er ikke klassificeret og antages i denne forbindelse at have egenskaber, der ligner 4methyl-2-pentanol (108-11-2). 
The substance is not classified and it is assumed in the present connection to have properties similar to those of 4-methyl-2-pentanol (108-11-2).
Dette stof er klassificeret R10 Xi; R37, og denne klassificering anvendes i nærværende screening. 
This substance is classified R10 Xi; R37, and the classification is used in the present screening.
Cresol er giftigt og ætsende og klassificeret T; C, R24/25-34. 
Cresol is toxic and corrosive and is classified T; C, R24/25-34.
I analyserne er der fundet en række ikke nærmere identificerede alifatiske kulbrinter med kædelængder på C10 til C16. 
In the analyses a number of not further identified aliphatic carbon hydrides have been detected with chain lengths of C10 to C16.
De kan være lineære eller forgrenede og have en eller flere dobbeltbindinger. 
They can be linear or branched and have one or more double bonds.
I listen over farlige stoffer er anført gruppen alkaner, C12-26. 
On the list on dangerous substances the group alkanes, C12-26, is mentioned.
For nærværende vurderes det derfor, at disse stoffer kan være kræftfremkaldende. 
At present it is therefore assessed that substances may be carcinogenic.
Stoffet tetramethyloctan kan være 2,2,7,7-tetramethyloctan. 
The substance tetramethyl octane may be 2,2,7,7-tetramethyloctan.
Sumformlen er C12H26 og kan derfor betegnes som hørende til gruppen af alifater C12-16. 
The molecular formula is C12H26 and can therefore be described as being part of the group of aliphates C12-16.
Tetramethyloctan-forbindelsen vurderes derfor sammen med de øvrige alifatiske kulbrinter. 
The compound of tetramethyl octane is therefore assessed along with the other aliphatic carbon hydrides.
I analyserne er der fundet en række aldehyder. 
In the analyses a number of aldehydes have been detected.
Disse er vist i tabel 4.2. 
They are shown in table 4.2.
Tabel 4.2 Aldehyder og deres egenskaber Navn 
Table 4.2 Aldehydes and their properties Name
Aldehyder er almindeligvis irriterende ved kontakt med hud og øjne og kan virke irriterende ved indånding. 
Aldehydes are generally irritating to skin and eyes and may be irritating to the respiratory system.
En del af aldehyderne anvendes som tilsætningsstoffer til fødevarer. 
A part of the aldehydes can be used as additives for food.
De stoffer, der er fundet i analyserne, og som betegnes potentielt problematiske, er vist i tabel 4.3. 
The substances, detected in the analyses, which are described as potentially problematic substances, are shown in table 4.3.
De data, der er anført med grå tone i tabel 4.3 er data, der er estimerede. 
The data, emphasised by a grey colour in table 4.3, are estimated data.
Tabel 4.3 omfatter de stoffer, der er kendt for eller mistænkt for at have langtidsvirkninger, og/eller hvor den målte koncentration udgør mere end 1 % af grænseværdien. 
Table 4.3 includes the substances, known for having or under suspicion of causing long-term effect and/or where the measured concentration constitutes more than 1 % of the TLV.
De er alene vurderet ud fra, at de kan være kræftfremkaldende. 
The hydrocarbons are solely assessed based on the fact that they may be carcinogenic.
Samtidig optræder de i en relativt høj koncentration. 
At the same time they appear in the analyses in a relatively high concentration.
Tabel 4.3 Liste over potentielt problematiske stoffer 
Table 4.3 List on potentially problematic substances Substance
Max/GV i % 
Max/TLV in %
Acetaldehyd 75-07-0 Fx;R12 
Acetaldehyde 75-07-0 Fx;R12
68-12-2 Rep2;R61 Xn;R20/21 Xi;R36 Formaldehyd 50-00-0 T;R23/24/25 C;R34 Carc3;R40 R43 
68-12-2 Rep2;R61 Xn;R20/21 Xi;R36 Formaldehyde 50-00-0 T;R23/24/25 C;R34 Carc3;R40 R43
Tetrachlorethylen 127-18-4 Carc3;R40 N;R51/53 Trimethylcyclohexen-1-on (isophoron) 
Tetrachlorethylen 127-18-4 Carc3;R40 N;R51/53 Trimethylcyclohexen-1-on (isophorone)
2- Butoxyethanol 111-76-2 Xn; R20/21/22 Xi; R36/38 
2- Butoxyethanole111-76-2 Xn; R20/21/22 Xi; R36/38
Som det ses af tabel 4.3 er der fundet relativt høje koncentrationer af dimethylformamid, formaldehyd og kulbrinter C10-C16 og phenol. 
As shown in table 4.3 the detected concentrations for dimethyl formamide, formaldehyde and hydrocarbons C10-C16 and phenol are relatively high.
I forhold til en sammenligning med grænseværdier udgør de målte koncentrationer mere end 1% af grænseværdien for 
Compared with the TLVs the measured concentrations represent more than 1% of the TLV of
Af de udvalgte stoffer er gruppen af hydrocarboner, alifater med kulstofkæder på C10-16 klassificeret kræftfremkaldende i kategori 2 (Carc2). 
Among the selected substances the group of hydrocarbons, aliphates with carbon chains at C10-16 are classified as carcinogenic in category 2 (Carc2).
Ethoxyethanol er reproduktionsskadende (Rep2;R60-61). 
Ethoxyethanole is teratogenic (Rep2; R60-61).
Dimethylformamid er ligeledes reproduktionsskadende (Rep2;R61). 
Dimethyl formamide is also teratogenic (Rep2; R61).
Af de udvalgte stoffer er følgende mistænkt for at kunne give kræft (Carc3;R40): 
Among the selected substances the following substance are under the suspicion of causing cancer (Carc3; R40):
Phenol er giftigt og ætsende. 
Phenol is toxic and corrosive.
Stoffet 2,6-di-tert-butyl-p-crecol har antagelig de samme egenskaber, og derfor er begge stoffer taget med. 
The substance 2,6-di-tert-butyl-p-crecol has probably the same properties and therefore both substances are mentioned.
Derudover er følgende stoffer udpeget som væsentlige efter aftale med Miljøstyrelsen: 
In addition the following substances are selected as being significant as agreed with the Danish EPA:
2-Butoxyethanol xylen toluen 
2-Butoxyethanol xylene toluene
4.3.2 Forekomsten af de potentielt problematiske stoffer 
4.3.2 The existence of potentially problematic substances
I den indledende screening er der taget udgangspunkt i de højest målte værdier. 
The preliminary screening is based on the highest measured values.
I tabel 4.4 er vist, i hvilke produkter disse stoffer forekommer og i hvilke koncentrationer. 
Table 4.4 shows in which products the substances are found and in which concentrations.
må anses for usikkerheder/forureninger. 
considered uncertainty/pollutants
Analyseresultaterne vist i tabel 4.4 er korrigeret for blindværdier. 
The results of analyses shown in table 4.4 are adjusted according to the blind values.
Tabel 4.4 Oversigt over analyseresultater for prioriterede stoffer. 
Table 4.4 Overview of results of the analyses on selected substances.
Acetaldehyd 75-07-0 α-Pinen 
Acetaldehyde 75-07-0 α-Pinene
Trimethylcyclohexen-1-on (isophoron) 
Trimethylcyclohexen-1-on (isophorone)
I prøve A er der primært fundet dimethylformamid, 2,6-di-tert-butyl-p-cresol, formaldehyd samt alifatiske kulbrinter. 
In sample A, the substances detected are primarily dimethyl formamide, 2,6-di-tert-butyl-p-cresol, formaldehyde and aliphatic hydrocarbons.
I prøve B er fundet en høj koncentration af formaldehyd og alifatiske kulbrinter. 
In sample B a high concentration of formaldehyde and aliphatic hydrocarbons have been detected.
Dertil kommer 3-caren og α-pinen, der kan forårsage overfølsomhed ved hudkontakt. 
In addition 3-caren and α-pinene have been detected as well, which may cause sensitisation by skin contact.
I prøve C er fundet høje koncentrationer af formaldehyd og alifatiske kulbrinter. 
In sample C high concentrations of formaldehyde and aliphatic hydrocarbons have been detected.
Dertil kommer acetaldehyd, der er mistænkt for at være kræftfremkaldende. 
In addition acetaldehyde has been detected, which is under suspicion of causing cancer.
Prøve D er karakteriseret ved høje koncentrationer af 2-Butoxyethanol, formaldehyd og alifatiske kulbrinter. 
Sample D is characterised by high concentrations of 2-Butoxyethanol, formaldehyde and aliphatic hydrocarbons.
Dimethylformamid, der forekommer i en relativt begrænset mængde, er reproduktionsskadende. 
Dimethyl formamide, which is present in relatively small quantities, is teratogenic.
Ligeledes er der fundet små mængder acetaldehyd og tetrachlorethylen, der er mistænkt for kunne give kræft. 
Likewise small quantities of acetaldehyde and tetrachloroethylen, which are under the suspicion of causing cancer, have been detected.
Prøve E er karakteriseret ved en vis koncentration af alifatiske kulbrinter, der er kræftfremkaldende, og dimethylformamid, der er reproduktionsskadende. 
Sample E is characterised by a certain concentration of aliphatic hydrocarbons, which are carcinogenic, and of dimethyl formamide, which is teratogenic.
Ligeledes er der konstateret formaldehyd og trimethylcyclohexen-1-on, der er mistænkt for at være kræftfremkaldende. 
Likewise formaldehyde and trimethylcyclohexen-1-on, which are under suspicion of causing cancer, have been detected.
Prøve F er primært karakteriseret ved høje koncentrationer af alifatiske kulbrinter, der er kræftfremkaldende. 
Sample F is primarily characterised by high concentrations of aliphatic hydrocarbons, which are carcinogenic.
2-Ethoxyethanol, der forekommer i en vis mængde, og dimethylformamid, der forekommer i en relativt lav koncentration, er begge reproduktionsskadende. 
2-Ethoxyethanol, which is present in a certain quantity, and dimethyl formamide, which is present in a rather low concentration, are both teratogenic.
Formaldehyd, der er mistænkt for at være kræftfremkaldende, forekommer i en relativt lav koncentration. 
Formaldehyde, which is under the suspicion of causing cancer, appears in a relatively low concentration.
Dertil kommer α-pinen, der kan medføre overfølsomhed ved hudkontakt. 
In addition α-pinene, which may cause sensitization by skin contact, is present.
De værdier, der er baseret på vurderinger, er i tabel 4.5 vist med grå baggrund. 
The values based on assessments are emphasised with a grey background in table 4.5.
Vurderingen er anført i afsnit 4.2.1. 
The assessment is mentioned in subsection 4.2.1.
Tabel 4.5 Oversigt over mindre væsentlige stoffer i screeningen 
Table 4.5 Overview on less significant substances detected in the screening
Klassificering- Listen over farlige stoffer 
Classification- List on dangerous substances
Vejledend e liste til klassificering 
Guidelines for classificati on
Max målt værdi mg/m 
Max measured value mg/m
Max/GV i % 
Max/GV in %
5131-66-6 Xi; R36/38 hvis > 20% 
5131-66-6 Xi; R36/38 if > 20%
67-64-1 F; R11 Xi; R36-66-67 Benzaldehyd 100-52-7 Xn, R22 Butanal 
67-64-1 F; R11 Xi; R36-66-67 Benzaldehyde 100-52-7 Xn, R22 Butanal
Cyclohexanon 108-94-1 R10 Xn; R20 Decanal 
Cyclohexanone 108-94-1 R10 Xn; R20 Decanal
Som det ses af tabel 4.5, er der ingen af de viste stoffer, der er kendt eller mistænkt for at have sundhedsmæssige langtidsvirkninger. 
As shown in table 4.5, none of the listed substances are known or under suspicion of having any long-term effects on the health.
Dertil kommer, at de højest målte koncentrationer udgør mindre end 1% af grænseværdien. 
In addition, the highest measured concentrations pose less than 1% of the limit value.
De stoffer, der er vist i tabel 4.5 vurderes ikke videre. 
The substances shown in table 4.5 will not be assessed any further.
Det er målet at foretage en vurdering af, om der sker en påvirkning af børn ved leg med de analyserede produkter. 
The purpose of assessing the substances is to decide whether children may be affected by using the analysed products.
Der anlægges en worst case betragtning. 
The assessment is based on a worst case scenario.
Principperne for vurderingen af sundhedsrisiko er baseret på EU's reviderede Technical Guidance Document (TGD) for risikovurderinger. 
The principles for the assessment of health effects are based on EU's revised Technical Guidance Document (TGD) for risk assessments.
Analyseresultaterne har vist, hvilke mængder af de pågældende stoffer, der afgives fra de enkelte produkter. 
The results of the analyses show the quantities of the substances in question, which are released from each product.
Den mængde, et barn kan risikere at indånde og optage, vurderes. 
The quantity that a child may be exposed to by inhalation is assessed.
I de tilfælde, hvor det har været muligt at finde data for NOAEC (No Observed Adverse Effect Concentration) og/eller LOAEC (Lovest Observed Adverse Effekt Concentration), er disse direkte sammenlignet med de målte koncentrationer. 
For those substances for which it has been possible to retrieve data for NOAEC (No Observed Adverse Effect Concentration) and/or LOAEC (Lowest Observed Adverse Effect Concentration), a direct comparison has been made with the measured concentrations.
Den mængde stof, et barn kan optage, er beregnet ud fra følgende forudsætninger. 
The quantity of the substance that a child may absorb is estimated based on the following conditions.
Der tages udgangspunkt i, at et barn kan have en legemsvægt på ned til 10 kg. Dette er en konservativ antagelse, der er hente fra TGD'en. 
It is assumed that a child may have a body weight as low as 10 kg. The assumption is conservative has been retrieved from the TGD.
Der foretages en vurdering ud fra den højeste målte koncentration, der forekommer tre timer efter udpakning af produktet. 
An assessment is made based on the highest measured concentration occurring three hours after the product has been unpacked.
Giver denne anledning til betænkeligheder, inddrages de øvrige analyseresultater, der er målt 3, 10 og 28 døgn efter udpakning af produktet. 
If it gives reason to assess the substance further the other analysis results measured at 3, 10 and 28 days after the product has been unpacked will be taken into account.
Mængden af inhaleret stof kan bestemmes efter retningslinierne i TGD (2002) efter formlen: 
The quantity of the inhaled substance can be determined according to the guidelines in TGD (2002) using the formula:
Mængde af inhaleret stof målt i mg/kg legemsvægt/dag 
The quantity of inhaled substance measured in mg/kg body weight/day
Inhalerbar eller respirabel fraktion af stoffet 
Amount absorbed by inhalation or respirable fraction of the substance
Inhalationsrate målt i m 3/time 
Inhalation rate measured in m3/time
Varighed af eksponeringen målt i timer 
Duration of the exposure measured in hours
Andelen af inhalerbar eller respirabel fraktion, Fresp, sættes til en given fraktion, såfremt data er tilgængelige. 
BW Body weight measured in kg The part of absorbed or respirable fractions, Fresp, is fixed at a given fraction if data are available.
I modsat fald sættes den til 1. 
If not the fraction is fixed at 1.
Varigheden af eksponeringen sættes til 1 time (Tcontact) og antal gange pr dag (Nevent) sættes ligeledes til 1. 
The duration of exposure is fixed at 1 hour (Tcontact) and the number of times per day (Nevent) is also fixed at 1.
Et barns legemsvægt sættes til 10 kg. 
The body weight of a child is fixed at 10 kg.
Stoffets kogepunkt er 171-172°C (Budavari, S., 1989) og dets smeltepunkt er -70°C (American Conference of Governmental Industrial Hygienists; 1986). 
The boiling point of the substance is 171-172°C (Budavari, S., 1989) and its melting point is -70°C (American Conference of Governmental Industrial Hygienists; 1986).
2-butoxyethanol er optaget på listen over farlige stoffer og klassificeret under EU index nr. 603-014-00-0 (Listen over farlige stoffer, Miljøministeriet 2002): 
2-butoxyethanol is included on the list on dangerous substances and is classified under EU index no 603-014-00-0 (List over dangerous substances, Miljøministeriet 2002):
Fra dyreforsøg er det set, at stoffet absorberes hurtigt ved indånding, indtagelse eller hudkontakt, og at det omsættes til 2-butoxyacetaldehyd og 2butoxy eddikesyre. 
In an animal experiment it is shown, that the substance is absorbed quickly by inhalation, if swallowed or in contact with skin and that it is decomposed to 2-butoxyacetaldehyd and 2-butoxy acetic acid.
Den primære effekt er, at stoffet og dets metabolitter er hematoksiske (virker på hæmoglobinet i blod). 
The primary effect is that the substance and its metabolites are hematoxic (affect the haemoglobin in blood).
I rotter er blivende effekter set på centralnervesystemet, lever og nyrer ved højere koncentrationer (kilden angiver ikke mængden). 
In rats the effects detected in the central nervous system, liver and kidneys are permanent at high concentrations (the source does not mention the quantity).
Stoffet virker ikke sensibiliserende, og der foreligger ikke indikationer af, at stoffet er mutagent (World Health Organization, 1998). 
The substance does not cause sensitisation and no data indicate that the substance is mutagenic (World Health Organization, 1998).
I et 13 ugers forsøg udført af NTP (1993) testede man rotter. 
In a 13 weeks experiment prepared by NTP (1993) rats were tested.
Man observerede skader på blod og knoglemarv og bestemte LOAEL til mellem 69 og 82 mg/kg/dag. 
Damages on the blood and the bone marrow were observed and the LOAEL was determined to be between 69 and 82 mg/kg/day.
I rapporten over risikovurdering af legetøj (CEN/TC 52/WG9, 2003) er der anført en værdi for TDI (tolerable daily intake) på 0,05 mg/kg. 
In the report on risk assessment of toys (CEN/TC 52/WG9, 2003) a value for TDI (tolerable daily intake) of 0.05 mg/kg is stated.
For 2-butoxyethanol antages det, at 100% af dampene inhaleres og optages (Fresp. 
As for 2-butoxyethanol it is assumed that 100% of the vapour is inhaled and absorbed (Fresp.
Den bestemte LOAEL ligger på mere end 1000 gange den beregnede inhalerede mængde. 
The determined LOAEL is more than 1000 times the estimated inhaled quantity.
TDI-værdien ligger lidt over den beregnede værdi. 
The TDI-value is a little above the estimated value.
Det må derfor vurderes, at udsættelse for stoffet i de aktuelle koncentrationer har en minimal sundhedsmæssig betydning. 
It is therefore assessed that exposure of the substance in the mentioned concentrations has a minimal influence on the health.
Stoffets kogepunkt er 135°C (Lide, D.R., 1994-1995) og dets smeltepunkt er -70°C (Kirk-Othmer Encyclopedia of Chemical Technology,1980). 
The boiling point of the substance is 135°C (Lide, D.R., 1994-1995) and its melting point is -70°C (Kirk-Othmer Encyclopedia of Chemical Technology, 1980).
Rep2; R60-61 Kan skade forplantningsevnen Kan skade barnet under graviditeten 
Rep2; R60-61 May impair fertility May cause harm to the unborn child
2-ethoxyethanol er fundet lidt irriterende ved øjenkontakt og ved slimhindekontakt, hvorimod der ikke er konstateret irritationer ved hudkontakt (Clayton, G. 
2-ethoxyethanol may be slightly irritating in contact with eyes and mucous membrane, however, there are no indications saying that it may be irritating in contact with skin (Clayton, G.
Den dødelige dosis for mennesker er omkring 1,4 ml/kg svarende til omkring 100 ml for en person på 70 kg (Amdur et al., 1991). 
The lethal dose for humans is about 1.4 ml/kg conforming with about 100 ml for a human weighing 70 kg (Amdur et al., 1991).