natgillin/translations-raw huggingface dataset:
I bilag 6 er rådata og henfaldskurver for alle forsøg vedlagt. 
Raw data and curves of decay of all tests are available in appendix 6.
Tabel 6.8: Emitterede stoffer og emissionsparametre for tekstiler renset med kulbrintebaserede rensermidler -: 
Table 6.8: Emitted chemicals and emission parameters for textiles dry-cleaned using hydrocarbonbased cleaning fluids -:
Afdampning af rensemidler ikke påvist 
Evaporation of cleaning fluids not demonstrated
Kulbrinteblanding, C10-C15 
Hydrocarbon compound, C10-C15
Korrelationskoefficient R0: Initial emissionsrate k: 
Correlation coefficient R0: Initial emission rate k:
Glycoletherne udgøres af en multikomponent blanding med 3-4 enkeltkomponenter. 
The glycolethers consist of a multi component mixture with 3-4 single components.
Den primære komponent er en isomerblanding af dipropylenglycolt-butylether (CAS nr. 132739-31-2). 
The primary component is an isomer compound of dipropylenglycol-t-butylether (CAS number 132739-31-2).
Der er i alle prøver med indhold af glycolethere endvidere påvist butoxyethoxyethanol. 
In all samples containing glycolethers, the content of butoxyethoxyethanol has been demonstrated.
I prøver fra rensninger med glycoletherbaserede rensemidler var mængden af butoxyethoxyethanol mindre end 1% af den samlede mængde glycolethere, mens butoxyethoxyethanol udgjorde mellem 3 og 20% af glycolethermængden i tekstiler, hvor det primære rensemiddel er kulbrintebaseret. 
In samples from dry-cleaning using glycolether-based cleaning fluids, the quantity of butoxyethoxyethanol was smaller than 1% of the total quantiy of glycolethers, whereas butoxyethoxyethanol made up between 3 and 20% of the glycolether quantity in textiles where the primary cleaning fluid is hydrocarbon-based.
6.7.2 Restindhold af alkylphenolpolyethoxylater De gennemførte analyser for alkylphenolpolyethoxylater før og efter rensning af tekstilerne har givet følgende resultater. jf. tabel 6.10 og 6.11. 
6.7.2 Residue of alkylphenolpolyethoxylates The analyses for alkylphenolpolyethoxylates before and after the dry-cleaning of the textiles have given the following results (table 6.10 and 6.11).
Resultaterne er korrigeret for blindværdier (indhold før rensning). 
The results have been corrected for blind values (content before dry-cleaning).
Tabel 6.10: Restindhold af alkylphenolpolyethoxylater efter rensning (kulbrintebaserede rensemidler). 
Table 6.10: Residue of alkylphenolpolyethoxylates after dry-cleaning (hydrocarbon-based cleaning fluids).
7.1 Opstilling af matematisk model 
7.1 Development of a mathematical model
Formålet med fase 4 er at opstille en simpel metode til omregning af afdampningshastighederne for de fundne komponenter bestemt ved klimakammermålingerne i fase 3 til resulterende koncentrationer (bidrag) af disse i boligers indeluft. 
The purpose of phase 4 is to set up a simple method for conversion of the evaporation speeds of the components determined by measurements in climatic chambers in phase 3 into resulting concentrations (contribution) in the indoor air of residences.
Data fremskaffet i fase 3 anvendes sammen med modellen til eksemplificering af indeklimakoncentrationer ved introduktion af renset tøj i boligen. 
The data provided in phase 3 will be used together with the model for exemplification of the indoor climate concentrations when introducing dry-cleaned clothes into the residence.
Sinkeffekter beskriver det forhold, at bygningsdele og interiør adsorberer og desorberer kemikalierne. 
Elimination of adsorption/desorption in the model means that the maximum concentrations from the calculations are probably overestimated.
· Det antages videre, at effekten af temperatur- og luftfugtighedsvariationer på emissionen af komponenterne fra renset tøj er ubetydelige, idet emissionsparametrene fundet i nærværende projekt er bestemt ved typiske indeklimaforhold. 
· It is also assumed that the effect of the temperature and atmospheric humidity variations in the emission of the components from drycleaned clothes is insignificant, as the emission parameters found in this project have been determined under typical indoor climate conditions.
· Det antages, at det rensede tekstil er taget ud af posen og opbevares frit i rummet. 
· It is assumed that the dry-cleaned textile is taken out of the bag and is kept freely in the room.
Det antages videre, at tøjet forbliver i rummet/boligen i hele emissionsperioden. 
It is also assumed that the clothes remain in the room/ residence throughout the whole emission period.
Med udgangspunkt i førnævnte antagelser kan der opstilles en ”single chamber unsteady state” massebalance for situationen, hvor der introduceres renset tekstil i boligen. 
Based on the above assumptions, a ”single chamber unsteady state” mass balance can be set up for the situation where dry-cleaned textile is introduced into the residence.
Der opstilles indledningsvis en model for den situation, at der introduceres ét stykke renset tekstil til boligen. 
Initially, a model is developed for the situation where one piece of dry-cleaned textile is introduced into the residence.
Herefter opstilles en model, hvor det antages, at der på samme tid er introduceret flere typer af renset tekstil til boligen. 
Then, a model is developed where it is assumed that more types of dry-cleaned textile are introduced into the residence at the same time.
Endelig diskuteres størrelsen af startværdien (baggrundskoncentrationen). 
Finally, the size of the starting value (background concentration) is discussed.
7.1.1 Model for introduktion af ét stykke renset tekstil 
7.1.1 Model for introduction of one piece of dry-cleaned textile
Følgende massebalance danner udgangspunkt for modellen til beregning af den resulterende koncentration i indeklimaet efter introduktion af én type renset tekstil: 
The following mass balance forms the basis of the model for calculation of the resulting concentration in the indoor climate upon introduction of one type of dry-cleaned textile:
(2) Ændring i masse = masse emitteret - masse fjernet 
(2) Change in mass = mass emitted - mass removed
7.1.2 Model for introduktion af flere typer renset tekstil 
7.1.2 Model for introduction of more types of dry-cleaned textile
Hvis der introduceres forskellige typer af renset tøj med forskellige emissionsstyrende parametre (Ro, k) samtidigt i boligen, ser massebalancen ud som følger: 
If various types of dry-cleaned clothes with different emission controlling parameters (Ro, k) are introduced simultaneously in the residence, the mass balance will look as follows:
Ydermere gennemføres beregninger for den situation, hvor det rensede tekstil emitterer i en stor velventileret bolig. 
The value is assumed to be representative of a non-affected background level in both single-family houses and apartments.
Koncentration af komponent i indeluften 
Indoor air concentration of component
Det bemærkes, at luftkvalitetskriterierne ikke kan anvendes i forbindelse med vurdering af, hvad der er en acceptabel eller uacceptabel udsættelse i forbindelse med indeklimapåvirkninger som følge af privatpersoners forbrugsmønstre, herunder hjembringelse af renset tekstil. 
Please note that the air quality criteria cannot be used for estimating what is an acceptable or unacceptable exposure in connection with the indoor climate influences as a result of the consumption patterns of private persons, including bringing home dry-cleaned textile.
Da der ikke foreligger et luftkvalitetskriterium for den primære glycolether dipropylen-tert-butylether (CAS nr. 132739-31-2) er den samlede eksponering af glycolethere er foretaget relativt i forhold til størrelsesordenen af luftkvalitetskriteriet for dipropylenglycol-butylether (CAS nr. 29911-28-2). 
As there is no air quality criterion for the primary glycolether dipropylen-tertbutylether (CAS number 132739-31-2), the total exposure of glycolether is made relatively in relation to the air quality criterion for dipropylenglycolbutylether (CAS number 29911-28-2).
Som det fremgår af afsnit 6.7 er der i klimakammermålingerne på alle Rynexrensede tekstiler påvist glycolethere. 
As it appears from section 6.7, glycolethers have been demonstrated in all Rynex dry-cleaned textiles during all measurements made in climatic chambers.
Ydermere er der konstateret spor af tetrachlorethylen fra jakken og bukserne, mens tetrachlorethylenafgivelsen fra kjolen var målbar. 
Furthermore, the jacket and trousers bore traces of tetrachlorethylen, whereas liberation of tetrachlorethylen from the dress could be measured.
I tabel 7.1 er opsummeret modelresultaterne for emissionen af glycolether fra Rynex-renset tekstil. 
Table 7.1 shows the model results for the emission of glycolether from Rynex dry-cleaned textile.
Tabel 7.1: Modelberegninger af den resulterende koncentration af glycolethere (regnet som dipropylengycol-butylether) som følge af Rynex-renseprocessen. 
Table 7.1: Model calculations of the resulting concentration of glycolethers (dipropylengycol-butylether) as a result of the Rynex dry-cleaning process.
B: Vurderet relativt til Miljøstyrelsens luftkvalitetskriterium for di-propylenglycolbutylether (Cas nr. 29911-28-2). 
Estimated relatively to the air qualtiy criterion of the Danish Environmental Protection Agency for di-propylenglycol-butylether (CAS number 29911-28-2).
Rynex-renset tekstil Emission af glycolethere 
Rynex dry-cleaned textile Emission af glycolethers
Antal habitter (jakke og bukser) 
Number of suits (jacket and trousers)
Gennemsnitlig indeklimakoncentration mg/m 
Average indoor climate concentration mg/m
Maksimal koncentration, mg/m 
Air quality criterion
Foretages beregningen på et fuldt opblandet parcelhus, viser resultaterne, at koncentrationen af rensevæske i indeklimaet vil være mindre end luftkvalitetskriteriet for di-propylenglycol-butylether. 
If the calculation is made for a completely mixed single-family house, the results show that the concentration of cleaning fluid in the indoor climate will be smaller than the air quality criterion for di-propylenglycol-butylether.
Beregningerne viser, at koncentrationen i indeklimaet vil være i samme størrelsesorden som luftkvalitetskriteriet for di-propylenglycol-butylether efter typisk 1-2 uger, såfremt der er tale om dårligt ventilerede forhold og efter få dage, såfremt der er tale om velventilerede forhold. 
The calculations show that the size of the concentration in the indoor climate will be identical to the size of the air quality criterion for di-propylenglycolbutylether after typically 1-2 weeks in case of poorly ventilated conditions and after a few days in case of well-ventilated conditions.
Det kan således ikke udelukkes, at der kan forekomme indeklimaproblemer som følge af afgivelse af glycolethere fra Rynex-renset tekstil til boliger. 
Therefore, indoor climate problems may occur due to emission of glycolether from Rynex dry-cleaned textile for residences.
Gennemføres beregningerne for afgivelse af tetrachlorethylen fra den Rynexrensede kjole, kan det vises, at koncentrationsbidraget af tetrachlorethylen fra kjolen til indeklimaet i et rum i en dårligt ventileret lejlighed ikke på noget tidspunkt overskrider 0,2 mg/m 
If the calculations are made for emission of tetrachlorethylen from the Rynex dry-cleaned dress, it can be demonstrated that the concentration contribution of tetrachlorethylen from the dress to the indoor climate in a room of a poorly ventilated apartment will never exceed 0.2 mg/m
3. Til sammenligning kan nævnes, at luftkvalitetskriteriet for tetrachlorethylen er 6 mg/m 
3. It this connection, it can be mentioned that the air quality criterion for tetrachlorethylen is 6 mg/m
Jævnfør afsnit 6.7 viste klimakammermålingerne afgivelse af kulbrinter og glycolethere fra kulbrinte-rensede bukser og jakke. 
According to section 6.7, the measurements carried out in the climatic chambers showed emission of hydrocarbons and glycolethers from the hydrocarbon dry-cleaned trousers and jacket.
Der kunne ikke påvises afgivelse af tetrachlorethylen fra de nævnte tekstiler. 
No emission of tetrachlorethylen from the mentioned textiles could be demonstrated.
Ved målinger på kjolen kunne ikke konstateres målbar afgivelse af nogen af de nævnte stoffer. 
It was not possible to measure any emission of the above substances from the dress.
Resultaterne af modelberegningerne fremgår af nedenstående tabel 7.2 og 7.3 for hhv. kulbrinter og glycolethere afgivet fra kulbrinte-renset tekstil. 
The results of the model calculations appear from table 7.2 and 7.3 for hydrocarbons and glycolethers emitted from hydrocarbon dry-cleaned textile.
Tabel 7.2: Modelberegninger af den resulterende koncentration af kulbrinter fra kulbrinte-rensede tekstiler introduceret i indeluften. 
Tablel 7.2: Model calculations of the resulting concentration of hydrocarbons from hydrocarbon dry-cleaned textiles introduced into residences.
A: Det antages, at alle de rensede tekstiler opbevares i dette rum. 
A: It is assumed that all the dry-cleaned textiles are kept in this room.
B: Miljøstyrelsens luftkvalitetskriterium for kulbrinter fra kulbrinte-rensevæske. 
B: The air quality criterion of the Danish Environmental Protection Agency for hydrocarbons from hydrocarbon cleaning fluid.
Kulbrinte-renset tekstil Emission af kulbrinter 
Hydrocarbon dry-cleaned textile Emission of hydrocarbons
Lille, dårligt ventileret lejlighed 
Small poorly ventilated apartment
Maksimal koncentration, mg/m Luftkvalitetskriterie 
Maximum concentration, mg/m Air quality criterion
Antal dage fra introduktion af renset tekstil til koncentrationen er i samme størrelsesorden som luftkvalitetskriteriet 
Number of days from introduction of drycleaned textile till the size of the concentration is identical to the size of the air quality criterion
Beregningerne viser, at ved de fundne residualindhold af kulbrinter i de kulbrinte-rensede tekstiler opnås koncentrationsbidrag for begge scenarier, der som gennemsnit kun udgør få mg/m 
The calculations show that the found residual content of hydrocarbons in the hydrocarbon dry-cleaned textiles results in average concentration contributions for both scenarios of only a few mg/m
3. Koncentrationerne når på intet tidspunkt op på koncentrationer i samme størrelsesorden som luftkvalitetskriteriet på 0,6 mg/m 
3. The concentrations never reach the size of the air quality criterion of 0.6 mg/m
Forestiller man sig, at der introduceres 3 kulbrinte-rensede habitter til et rum i en lille dårligt ventileret lejlighed opnås et koncentrationsbidrag af kulbrinter til rummet på 19 mg/m 
If you introduce 3 hydrocarbon dry-cleaned suits into a room of a small poorly ventilated apartment, you will get an average concentration contribution of hydrocarbons of 19 mg/m
som et gennemsnit over 1 uge med en maksimums 
in the room over a period of 1 week with a
værdi på 41 mg/m 
maximum value of 41 mg/m
få timer efter rensningen. 
a few hours after the dry-cleaning.
Tabel 7.3: Modelberegninger af den resulterende koncentration af glycolethere fra kulbrinte-rensede tekstiler introduceret i indeklimaet. 
Table 7.3: Model calculations of the resulting concentration of glycolethers from hydrocarbon dry-cleaned textiles introduced into residences.
: Det antages, at alle de rensede tekstiler opbevares i dette rum. 
: It is assumed that all the dry-cleaned textiles are kept in this room.
Vurderet relativt til Miljøstyrelsens luftkvalitetskriterium for di-propylenglycolbutylether (Cas nr. 29911-28-2). 
Estimated relatively to the air quality criterion of the Danish Environmental Protection Agency for di-propylenglycol-butylether (CAS number 29911-28-2).
8.1 Kemiske stoffer anvendt i kulbrinte- og Rynex-renserier 
8.1 Chemicals used in hydrocarbon and Rynex dry-cleaning shops
Som det fremgår af afsnit 4 anvendes der et stort antal kemikalieprodukter i de alternative renserier. 
As it appears from section 4, a large number of chemical products are used in the alternative dry-cleaning shops.
Kemikalierne har forskellige funktioner i renseprocessen, men gennemgang af sikkerhedsdatablade for de anvendte kemikalieprodukter viser, at der er visse kemikalier som ofte indgår i produkterne. 
The chemicals have different functions in the dry-cleaning process, but the safety data sheets of the chemical products used show that some of the chemicals appear frequently in the products.
Således ses eksempelvis 2-(2-butoxyethoxy)ethanol (CAS nr. 112-34-5), poly(oxy1,2-ethanediyl) (CAS nr. 69011-36-5) samt isoalkaner og isoparafiner ofte i produkterne. 
Some of these chemicals are 2-(2-butoxyethoxy)ethanol (CAS number 11234-5), poly(oxy-1,2-ethanediyl) (CAS number 69011-36-5), isoalkanes and isoparaffins.
Det høje antal af produkter anvendt i renserierne gør det vanskeligt, uden væsentligt forudgående kendskab til det aktuelle renseris drift, at forudsige f.eks. residualindhold i tekstilerne, affaldssammensætninger eller komponenter i forbindelse med en eventuelle jord- og grundvandsforureninger, se også afsnit 
The many products used in the dry-cleaning shops makes it difficult, without previous knowledge of the operation of the dry-cleaning shop in question, to predict for instance the residual content in the textiles, the residual compositions or components in connection with any soil and ground water pollutions.
Produkterne indeholder typisk kulbrinter eller glycolethere som dominerende komponent. 
The products typically contain hydrocarbons or glycolethers as the dominant component.
Ét produkt indeholder såvel kulbrinter som en glycolether. 
A product contains both hydrocarbons and glycolether.
Der er påvist indhold af N,N-dimethylalkylaminer i 2 af 13 produkter ved de gennemførte screeninger. 
N,N-dimethylalkyl amines have been found during the screenings in 2 out of 13 products.
I modsætning til resultaterne gengivet i Hohenstein (1996), se også tabel 4.4, kunne der ikke ved nærværende analyser af Frankotex HCR/KW påvises indhold af chlorerede opløsningsmidler. 
Contrary to the results from Hohenstein (1996) - please see table 4.4 - the present analyses of Frankotex HCR/KW did not demonstrate any chlorinated solvents.
Mængden af tetrachlorethylen i Rynex 2 og Cetox KWI udløser ikke krav om mærkning på databladet for produktet. 
Due to the small concentration of tetrachlorethylen in Rynex 2 and Cetox KWI, the data sheets of the products does not have to be marked.
Analyserne har vist et betydeligt antal flygtige/semi-flygtige stoffer, som enten ikke er mærkningspligtige eller som findes i så lave koncentrationer, at det ikke udløser mærkning. 
The analyses have shown a considerate number of volatile/semi-volatile substances that do not have to be marked according to law or they appear in such low concentrations that they do not have to be marked.
Analysen viste 1,1 %(vægtprocent) glycolethere samt et indhold af nonylphenolpolyethoxylater svarende til mindre end 0,001 % (vægtprocent). 
The contact water contained glycolethere in a concentration of 1.1 % (percentage by weight) and nonylphenolethoxylates in a concentration of less than 0.001 % (percentage by weight).
Som det fremgår af afsnit 6.1.2 er der i nærværende undersøgelse anvendt et kulbrinte-renseri, som også tidligere har leveret renset tekstil til klimakammermålinger (Miljøstyrelsen, 2002a). 
As it appears from section 6.1.2, this investigation includes a hydrocarbon dry-cleaning shop that has earlier delivered dry-cleaned textile for measurements in climate chambers (the Danish Environmental Protection Agency, 2002a).
Forsøgene viser sammenlignelige emissionsratekonstanter i forhold til resultaterne fundet tidligere. 
The tests show comparable emission rate constants in relation to the results found earlier.
Det er imidlertid bemærkelsesværdigt, at residualindholdet af kulbrinter bestemt i nærværende undersøgelse er væsentligt lavere end residualindholdet fundet i lignende tekstiler efter rensning i samme renseri knap et år tidligere. 
It is, however, remarkable that the residual content of hydrocarbons determined in this investigation is considerably lower than the residual content found in similar textiles after dry-cleaning in the same dry-cleaning shop approximately one year earlier.
Forklaringen skal formodentlig findes i, at variationen i residualindhold er væsentlig afhængig af fibertyper, destillationsprocessen, de anvendte kemikalier samt tørreprocessen. 
The explanation may be that the variation in residual content is very dependent on fiber types, the distillation process, the chemicals used as well as the drying process.
Ved forespørgsel oplyste renseriejeren, at der har været foretaget optimeringer af bl. 
When asked, the drycleaning shop owner informed that the drying process has been optimized.
a. tørreprocessen, idet temperaturen er hævet med 5 
The temperature has been increased by 5
oC og at kraftige tekstiler såsom overtøj (som erfaringsmæssigt er sværest at tørre) generelt holdes for sig selv i en mindre chargestørrelse. 
oC and thick textiles such as coats (the drying time of which is long) are generally kept separately in a small charge size.
Det er derfor sandsynligt, at de lave residualindhold for flygtige komponenter i væsentligt omfang kan begrundes i disse optimeringer. 
It is therefore probable that the low residual content for volatile components to a large extent is due to these optimizations.
Det kan ikke udelukkes, at også andre forhold kan spille en rolle. 
However, other conditions may also play an important part.
Det ligger uden for nærværende projekt at afdække, hvilke af optimeringerne, der er årsag til de lave residualindhold. 
It is outside the scope of this project to investigate which of the optimizations result in the low residual content.
Da resultaterne viser, at det er muligt at opnå meget lave residualindhold ved kulbrinte-rensningerne anbefales det dog, at der gennemføres tiltag, således at disse erfaringer kan komme andre renserier til gode. 
As the results show that it is possible to reach a very low residual content via hydrocarbon dry-cleaning, it is recommended to take action so that other dry-cleaning shops can benefit from these experiences.
Da det erfaringsmæssigt er lettere at tørre tetrachlorethylen ud af de rensede tekstiler sammenlignet med glycolethere og kulbrinter, er det sandsynligt, at erfaringerne fra kulbrinte-renseriet også kan anvendes for de øvrige renserityper. 
As it notoriously is easier to dry tetrachlorethylen out of the dry-cleaned textiles than glycolethers and hydrocarbons, it is likely that the experiences from the hydrocarbon dry-cleaning shop can also be used for the other dry-cleaning types.
Indholdet af rensevæsker efter 14 dages afgasningsperiode fremgår af tabel 6.10 og 6.11. 
The content of cleaning fluids after an emission period of 14 days appears from table 6.10 and 6.11.
Som det fremgår, er der ikke påviselige mængder af kulbrinter tilbage i tekstilerne. 
As it can be seen, there are no demonstrable quantities of hydrocarbons left in the textiles.
Dette bekræfter ovennævnte konklusioner på baggrund af klimakammerforsøgene. 
This confirms the above conclusions on the basis of the climate chamber measurements.
Der er glycolethere tilbage i alle seks tekstiler efter rensning og afgasning i klimakammerne. 
Glycolethers are left in all six textiles after dry-cleaning and emission in the climate chambers.
Specielt kjolematerialet synes at tilbageholde store mængder glycolethere. 
Especially the dress textile seems to contain large quantities of glycolether.
Dette indikerer, at selv med optimeret tørring kan det være kompliceret at opnå fuldstændig fjernelse af glycolethere fra tekstilerne. 
This indicates that even with optimized drying, it can be complicated to remove the glycolethers from the textiles completely.
Indholdet af nonylphenolpolyethoxylater i den ene renseforstærker kunne genfindes i jakken og bukserne efter rensning på kulbrinterenseriet. 
The content of nonylphenolpolyethoxylates in one of the cleaning intensifiers could also be found in the jacket and the trousers after dry-cleaning in the hydrocarbon dry-cleaning shop.
8.4 Renseriprocessen - opkoncentration af flygtige komponenter i destillatet 
8.4 The dry-cleaning process - concentration of volatile components in the distillate