natgillin/translations-raw huggingface dataset:
Det er muligt at sætte resultaterne op og evt. klippe dem ind i div. Windowsprodukter i miljørapporter til kunder samt at trække data ud og regne videre på dem i et regneark. 
It is possible to arrange the results and paste them into different Windows applications for environmental reports for customers or to draw data and make further calculations with them in a spreadsheet.
Standard Excel-regneark, layout og decimaler bestemmes af brugeren. 
Standard Excel spreadsheet, layout and decimals defined by the user.
Brugen af partikler eller PM10 er bestemt af de grundlæggende modellers enheder. 
The use of particles or PM10 is defined by the units of the basic models.
Af resultatarket fremgår energiforbrug og emissioner: 
The result sheet shows energy consumption and emissions:
totalt for transporten 
for the total transport
De forskellige resultater kan bruges i forskellige sammenhænge. 
The different results may be used for different purposes.
Totaltallet kan bruges i miljørapporter, grønne regnskaber m.v., hvor der følges op på virksomhedens samlede miljødata. 
The total may be used in environmental reports, green accounts etc. where the total environmental data of the firm are accumulated.
Per km tallene kan hurtigt vise, hvor stor de enkelte transportformers miljøbelastning er per km for den givne transport. 
The figures per km show the environmental load of the actual transport per km.
Til brug for tildeling af miljøbelastning til produkter er opgørelsen per ton velegnet, idet tallet kan følge produktet og blive lagt sammen med de øvrige bidrag i kæden fra produktion, håndtering og distribution. 
For the allocation of environmental load on the products a calculation per ton is suitable, as the figure can follow the product and be added to the other contributions in the chain from production, handling and allocation.
Miljøbelastningen per ton kan også bruges til budgetformål. 
The environmental load per ton may also be used for budget purpose.
Opgørelsen per tonkm kan dels bruges til at sammenligne miljøeffektiviteten af forskellige transportformer, men er i høj grad også nyttig til at vurdere effektiviteten for forskellige udbydere indenfor samme transportform. 
The calculation of tonkm may partly be used for comparing the environmental efficiency of different transport modes, but it is also very useful for estimating the efficiency of different transport providers of the same transport mode.
Grunddata for beregningerne. 
Basic data for the calculations.
Hvor standardværdierne er ændret og for km/l står de oprindelige værdier til højre for det nye tal. 
Where standard values are changed and for km/l the original values are to the right of the new value.
En lang række faktorer har betydning for en transports samlede energiforbrug og emissioner. 
A large number of factors have significance to the total energy consumption and emissions of a transport.
Det er derfor vigtigt at få alle faktorer med, når man skal se på ændringer i udformningen af transporterne. 
It is therefore important to include all factors when looking at changes in the elaboration of the transports.
Et ændret afsendelsestidspunkt for godset kan således påvirke hele transportkæden. 
A change in time of dispatch of the goods may thus influence the entire transport chain.
Der kan være direkte indflydelse på både antal kørte km, den gennemsnitlige godsvægt på lastbilen, og % tomkørsel. 
There may be direct impact on both number of km covered, the average weight of goods on the truck and percentage of empty load.
Mere indirekte kan Euro-norm, filterteknologi og km/l blive påvirket, hvis der samtidig sker en ændring i leverandør. 
More indirectly the Euro-norm, filter technology and km/l may be influenced, when changing transport provider.
Videre i transportkæden kan det nye afsendelsestidspunkt medføre et andet valg af afsendelsesbanegård eller brug af en anden færgerute. 
Further in the transport chain the new time of shipment may imply a different station of departure or use of a different ferry service.
Optimering af godstransport er, som det fremgår af ovenstående eksempel, en kompleks opgave, der aldrig stopper. 
Optimisation of freight transport is, as appears of the above example, a complex task which is never ending.
OMIT giver ikke lette løsninger, men kan medvirke til at vise, om kursen er rigtig, mod mindre energiforbrug og emissioner per ton gods. 
OMIT does not deliver easy solutions, but it may contribute to an indication of whether or not the course is right towards less energy consumption and emissions for each ton of goods.
40 t lastbildata findes ikke p.t. i TEMA2000, hvorfor beregningerne baseres på en 48 ton lastbil. 
Data for a 40 tons truck are not available in TEMA2000 at present; therefore the calculations are based on a 48 tons truck.
Da disse to lastbiltyper og de transporter der indgår i på mange punkter er forskellige, medfører det en fejl. 
These two truck types and the transports they carry out being different in many ways causes errors in the result.
Ved brug af realiserede dieselforbrugstal i OMIT forventes det at denne fejl er uden betydning. 
Using realised diesel consumption figures in OMIT, these errors are expected to be insignificant.
Energiindhold i diesel er på 36,295 MJ/l - ved 42,7 MJ/kg diesel, 850 g / l diesel. 
The energy content in diesel is 36.295 MJ/l - at 42.7 MJ/kg diesel, 850 g / l diesel.
Km/l findes ved at dividere 36,295 med "Energy consumption in MJ per km" fra resultatarket. 
Km/l is found by dividing 36.295 by "Energy consumption in MJ per km" from the result sheet.
Der henvises til TEMA2000 for yderligere dokumentation. 
We refer to TEMA2000 for further documentation.
Beregningerne er baseret på simulering i TEMA2000 som vist i tabel 3. 
The calculations are based on simulation in TEMA2000 as showed in table 3.
Energiforbrug i MJ per km. 
Energy consumption in MJ per km.
Endelig kan det være praktisk at inkludere en kort for- eller eftertransport i OMIT, fremfor at skulle beregne den separat. 
Finally it may be useful to include a short pre- or end haulage in OMIT, rather than calculating it separately.
Da de forskellige motorer har forskellige emissionsprofiler vil det medføre en fejl. 
As the different engines have different emission profiles, it will cause an error.
Energiforbruget vil derimod blive korrekt hvis man tager udgangspunkt i de realiserede km/l og en fordeling af emissionerne på godset der følger modellen for 40 t lastbilerne. 
The energy consumption, however, will be correct, if you take basis in the realised km/l and distribute the emissions on the goods, which follow the model for the 40 tons trucks.
Dvs. at energiforbrug og emissioner fordeles på godset udfra dets andel af den gennemsnitlige godsvægt, eller ved volumengods udfra andelen af den transporterede volumen. 
Hence the energy consumption and emissions are distributed on the goods by its share of the average goods weight or when voluminous goods, by the share of the transported volume.
Opgørelsen omfatter alle kørte km således, at hvis den anvendte metode anvendes på alt gods der transporteres vil alle emissioner og energiforbruget fra den givne lastbil blive fordelt på godset. 
The calculation includes all driven km, and if the method is used for transported goods, all emissions and the energy consumption from the actual truck will be distributed on the goods.
(Der vil ikke blive "glemt" noget). 
(Nothing will be "forgotten").
Man kan få en idé om fejlen ved at anvende den angivne metode ved at se på tabel 5, hvor 40 ton data er sammenlignet med distributionslastbiler fra TEMA2000. 
You can get an idea of the error by using the mentioned method and look at table 5, where data for 40 tons is compared with distribution trucks from TEMA2000.
This chapter gives the details of the approach and data sources for the consumption and emission figures for rail transport in Europe. 
Thus it also appears that this approximate method can only be applied, when it is a matter of a limited part of the total transport.
Therefore a limited number of corridors for rail transport is defined. 
The attempt is to capture these typical and dominant transports while staying simple and user friendly.
The model recommended by the Danish Energy Agency, and default in the model is the socalled 200 % method. 
The model recommended by the Danish Energy Agency, and default in the model is the so called 200 % method.
Kortlægning af kemiske stoffer i forbrugerprodukter 
Survey of chemicals in consumer products
Kortlægning af kemiske stoffer i renset tekstil fra Rynex og kulbrinterenserier 
Mapping of chemicals in dry-cleaned textiles from Rynex and hydrocarbon dry-cleaning shops
RESUMÉ OG KONKLUSION 
SUMMARY AND CONCLUSION
2 BESKRIVELSE AF PROJEKTS INDHOLD OG LÆSEVEJLEDNING 
2 THE CONTENTS AND READING INSTRUCTIONS OF THE PROJECT
6 FASE 3 - RENSNING AF TEKSTILER OG BESTEMMELSE AF RESIDUALINDHOLD 
6 PHASE 3 - DRY-CLEANING OF TEXTILES AND DETERMINATION OF RESIDUAL CONTENT
7 FASE 4 - MODELLERING AF INDEKLIMAPÅVIRKNINGEN FRA RENSET TEKSTIL 
7 PHASE 4 - MODELLING OF THE INDOOR CLIMATE INFLUENCE FROM DRY-CLEANED TEXTILE
8.4 RENSERIPROCESSEN - OPKONCENTRATION AF FLYGTIGE 
8.4 THE DRY-CLEANING PROCESS - CONCENTRATION OF VOLATILE
KOMPONENTER I DESTILLATET 
COMPONENTS IN THE DISTILLATE
Bilag 1: Spørgeskema til renserierne - uudfyldt 
Appendix 1: Questionnaire for the dry-cleaning shops - not completed
Bilag 2: Spørgeskemabesvarelser fra renserierne 
Appendix 2: Responses to the questionnaires from the dry-cleaning shops
Bilag 2a: Rynex-renserier 
Appendix 2a: Rynex dry-cleaning shops
Bilag 2b: Kulbrinte-renserier 
Appendix 2b: Hydrocarbon dry-cleaning shops
Bilag 3: Bruttoliste over anvendte kemikalieprodukter 
Appendix 3: Gross list of used chemical products
Bilag 6: Analyseresultater - afgasningsforsøg 
Appendix 6: Analysis results - emission tests
Bilag 7: Analyse- og målemetoder 
Appendix 7: Analysis and measurement methods
Projektet er en del af en større undersøgelse af forskellige forbrugerprodukter med hovedtitlen: Kortlægning af kemiske stoffer i forbrugerprodukter 
This project forms part of a major investigation of different consumer products with the title: Mapping of chemicals in consumer products.
Undersøgelserne er iværksat med henblik på at kortlægge området og belyse befolkningens udsættelse for kemiske stoffer i forbrugerprodukter og risikoen forbundet herved. 
The investigations were initiated in order to map the above field and to examine the exposure of the population to chemicals in consumer products as well as the risk involved.
Projektarbejdet er gennemført af et tværfagligt team bestående af medarbejdere fra Eurofins Danmark A/S og Kampsax A/S. 
The project work was carried out by an interdisciplinary team consisting of employees from Eurofins Denmark A/S and Kampsax A/S.
Projektets succes har været helt afhængig af oplysninger fra renserier og leverandører til renserier. 
The success of the project has been fully dependent on information from drycleaning shops and their suppliers.
Der skal derfor rettes en særlig tak til de 6 danske renserier samt de 4 leverandører til danske renserier, som velvilligt har besvaret spørgsmål samt fremsendt sikkerhedsdatablade for og prøver af kemikalieprodukter mm. Endvidere skal der rettes en tak til Flemming Gordon Olsen, Sober Rens ApS - Texpert Allerød, som bl. 
We would therefore like to express our sincere gratitude to the 6 Danish dry-cleaning shops and the 4 suppliers that have provided us with responses, safety product sheets and samples of chemical products, etc. Furthermore, we would like to thank Flemming Gordon Olsen, Sober Rens ApS - Texpert Allerød, who assisted us to work out section
Projektets primære målgruppe er Miljøstyrelsen samt forbrugere af rensning af tekstiler, hvor der anvendes kulbrinte- eller Rynex-rensevæske. 
The primary target group of the project is the Danish Environmental Protection Agency and consumers who have their textiles dry-cleaned, using hydrocarbon or Rynex cleaning fluid.
Projektets resultater vil endvidere have interesse for danske amter, kommuner, rådgivningsfirmaer, embedslægeinstitutionerne og andre, der varetager forvaltning eller rådgivning i relation til de kemiske stoffer, som anvendes i renseribranchen. 
The results of the project will also be of interest to Danish counties, municipalities, consultancy firms, health institutions and others dealing with administration or consultancy in relation to the chemical substances used in the dry-cleaning trade.
Nærværende forbrugerprojekt belyser brugen af kemikalier i alternative renserier, renserier som anvender enten kulbrinteblandinger eller glycoletherblandinger (Rynex) som rensevæske. 
This consumer project deals with the use of chemicals in alternative drycleaning shops using either hydrocarbon compounds or or glycolether compounds (Rynex) as cleaning fluid.
Formålet med projektet er at kortlægge kemikalieprodukter anvendt i de alternative renserier, herunder disses indhold af kemiske stoffer; at bestemme koncentrationen af reststoffer i udvalgte tekstiler (også kaldet residualindholdet) renset i alternative renserier, samt vurdere restindholdenes potentielle påvirkning af indeklimaet ved introduktion af tekstilerne i boliger. 
The purpose of the project is to map the chemicals used in the alternative dry-cleaning shops, including the composition of the chemicals, to determine the concentration of residues in selected textiles (residual content) dry-cleaned in alternative dry-cleaning shops and to evaluate the potential influence of the residues on the indoor climate by introducing the textiles into residences.
Ved forespørgsel til leverandører af kemikalieprodukterne blev sikkerhedsdatablade fremskaffet, og en bruttoliste blev udarbejdet med angivelse af deklarerede indholdsstoffer, produktnumre og producenter mm. Af bruttolisten fremgår det, at visse af kemikalierne anvendes i flere produkter, f.eks. 2-(2butoxyethoxy)ethanol (CAS nr. 112-34-5), poly(oxy-1,2-ethanediyl) (CAS nr. 69011-36-5) samt en række kulbrinteblandinger (isoalkaner og isoparafiner). 
Safety data sheets were provided from the suppliers of the chemical products and a gross list was prepared, stating the declared substances, product numbers and producers, etc. From the gross list, it appears that some of the chemicals are used in several products, e.g. 2-(2butoxyethoxy)ethanol (CAS number 112-34-5), poly(oxy-1,2-ethanediyl) (CAS number 69011-36-5) and a number of hydrocarbon compounds (isoalkanes and isoparaffins).
Prøver af kemikalieprodukterne Toptrel HP, Actrel 3365-D, Frankotex KW, Rynex 2, Cetox KWI, Prenett Pur, Solxex 1, Solvex 2, Solvex 3, ClipComfort, Polysol, Preclin Odosorb og TempoRyn blev analyseret for indhold af flygtige komponenter samt indhold af nonyl- og octyl-phenolpolyethoxylat. 
It was analysed if samples of the chemical products Toptrel HP, Actrel 3365D, Frankotex KW, Rynex 2 , Cetox KWI, Prenett Pur, Solxex 1, Solvex 2, Solvex 3, ClipComfort, Polysol, Preclin Odosorb and TempoRyn contained volatile components, nonyl and octyl phenol polyethoxylates.
Der kunne generelt konstateres god overensstemmelse mellem de deklarerede indholdsstoffer i sikkerhedsdatabladene og de fundne komponenter ved analyserne af produkterne. 
Generally, there was coincidence between the declared substances in the safety data sheets and the components found during the analyses.
Alle de undersøgte produkter overholdt Miljøstyrelsens regler for oplysning om indholdsstoffer i forbindelse med klassificering og mærkning. 
All the investigated products did meet the rules of the Danish Environmental Protection Agency with regard to information about substances in connection with classification and marking.
Undersøgelsen viste, at produkterne til denne branche typisk indeholder kulbrinter eller glycolethere som dominerende komponent. 
The investigation showed that the products for this trade typically contain hydrocarbons or glycolethers as dominant components.
Ydermere blev der analyseret en prøve af kontraktvand fra et kulbrinterenseri. 
Futhermore a sample of contact water was analysed.
Analysen viste 1,1 %(vægtprocent) glycolethere samt 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).
Der blev ikke påvist indhold af kulbrinter eller tetrachlorethylen i koncentrationer over 0,01 % (vægtprocent). 
Hydrocarbons or tetrachlorethylene was not detected (detection limit was 0,01 percentage by weight).
To sæt ens tekstiler bestående af frakke, bukser og kjole blev renset i henholdsvis et Rynex-renseri og et kulbrinte-renseri. 
Two sets of identical textiles consisting of coat, trousers and dress were drycleaned in a Rynex dry-cleaning shop and a hydrocarbon dry-cleaning shop respectively.
Residualindholdet af udvalgte kemikalier blev bestemt ved hhv. afgasning i klimakammer samt ved ekstraktion af komponenterne fra tekstilerne. 
The residual content of selected chemicals was determined via emission in a climatic chamber and via extraction of the components from the textiles.
Residualindholdet i tekstiler renset i kulbrinte-renseriet var generelt væsentligt lavere end residualindholdet i tekstiler renset i Rynex-renseriet. 
The residual content in textiles dry-cleaned in the hydrocarbon dry-cleaning shop was generally much lower than the residual content in textiles drycleaned in the Rynex dry-cleaning shop.
Der kunne konstateres rester af tetrachlorethylen i tekstiler fra Rynex-rensningen. 
Residues of tetrachlorethylene were demonstrated in textiles from the Rynex dry-cleaning.
Resultaterne fra klimakammermålingerne blev anvendt i en matematisk model til bestemmelse af den resulterende koncentration af de flygtige stoffer i indeklimaet i hhv. en dårligt ventileret lejlighed og et velventileret parcelhus. 
The results from the measurements in the climatic chamber were used in a mathematical model for determination of the resulting concentration of the volatile substances in the indoor climate in a poorly ventilated apartment and in a well-ventilated single-family house respectively.
Beregningerne blev foretaget ved introduktion af almindeligt forekommende mængder af tekstiler i private hjem. 
The calculations were made by introducing common quantities of textiles into private homes.
Ud fra resultaterne af modelberegningerne vurderes det, at der for tekstiler med lignende residualindhold er risiko for indeklimaproblemer som følge af afgivelse af glycolethere fra Rynex-renset tekstil. 
Based on the results of the model calculations, it is estimated that there may be a risk of indoor problems in connection with textiles with a similar residual content due to emission of glycolether from Rynex dry-cleaned textile.
Der kunne ikke ved modelberegningerne konstateres en uacceptabel påvirkning af indeklimaet som følge af introduktion af kulbrinte-renset tekstil til boligen. 
No unacceptable influence on the indoor climate could be demonstrated via the model calculations when the hydrocarbon dry-cleaned textile was introduced into the residence.
Destillater udtaget fra rensemaskinen i et kulbrinte- og et Rynex-renseri blev analyseret for indhold af flygtige komponenter. 
It was analysed if distillates from dry-cleaning machines in hydrocarbon and Rynex dry-cleaning shops contained volatile components.
Kemikalierne i rensemidlerne kan ende som restindhold i det færdigt behandlede tekstil og dermed påvirke forbrugerne. 
The chemicals in the cleaning fluids may end as residue in the finally treated textile and thereby influence the consumers.
Samtidigt kan indholdet af f.eks. chlorerede opløsningsmidler i produkterne udgøre et troværdighedsproblem for denne del af branchen, idet flere af de alternative renserier reklamerer med at være "klorfrie". 
At the same time, the content of for instance chlorinated solvents in the products can be a reliability problem for this part of the trade, as several of the alternative dry-cleaning shops advertise their shops as being "chlorine-free".
Af disse grunde bør kemikalieleverandørerne indføre en forbedret deklaration af indhold af kritiske stoffer som f.eks. tetrachlorethylen i produkterne - også selvom indholdet ikke er så højt, at det udløser et krav om mærkning i henhold til myndighedernes regler. 
For these reasons, the suppliers of chemical products ought to introduce an improved declaration of the content of critical substances like for instance tetrachlorethylene in the products - also in the cases where the content is below the level requiring marking in accordance with the rules of the authorities.
Delresultater i undersøgelsen har vist, at der er mulighed for, at restindholdet i tekstiler efter rensning kan reduceres meget væsentligt ved forbedret tørreteknik. 
Part-results of the investigation have shown that the residue in textiles may be reduced considerably after the dry-cleaning by using an improved drying technique.
1 Projektets baggrund og formål 
1 Background and objective
Miljøstyrelsens har udbudt en række forbrugerprojekter, som har til formål at kortlægge kemiske stoffer i almindeligt anvendte forbrugerprodukter. 
The Danish Environmental Protection Agency has invited tenders for a number of consumer projects the purpose of which is to map chemical substances in ordinary consumer products.
Et af projekterne omhandler kortlægning af kemiske stoffer i renset tekstil. 
One of the projects includes mapping of chemical substances in dry-cleaned textile.
Projektet har fokus på de renserier i Danmark, som anvender alternative rensevæsker såsom kulbrinte-rensevæske og Rynex-rensevæske (baseret på glycolethere). 
The project focuses on the dry-cleaning shops in Denmark using alternative cleaning fluids such as hydrocarbon cleaning fluid and Rynex cleaning fluid.
Baggrunden for projektet er således et ønske om øget kendskab til de kemikalier, som indgår i renseprocessen, og som eventuelt kan genfindes i tekstilerne efter rensning og efterbehandling. 
The reason for the project is a wish to increase the knowledge of the chemicals used in the dry-cleaning process and which may be found in the textiles after dry-cleaning and final treatment.
· At kortlægge hvilke kemikalier, der indgår i produkterne ved såvel forespørgsler til leverandører og/eller producenter som kemiske analyser af udvalgte kemikalieprodukter. 
· To map which chemicals are included in the products, both by making inquiries at suppliers and/or producers and by carrying out chemical analyses of selected chemical products.
· At undersøge koncentrationen af reststoffer i udvalgte tekstiler efter rensning med de alternative rensevæsker. 
· To investigate the concentration of residual substances in selected textiles upon dry-cleaning using the alternative cleaning fluids.
· At vurdere den potentielle påvirkning af indeklimaet ved introduktion af renset tekstil i boliger. 
· To estimate the potential influence on the indoor climate by introducing dry-cleaned textile into residences.
Såvel i ovenstående tekst, som i resten af rapporten skal der med ”renseri” forstås et renseri, der anvender kulbrinteblanding eller Rynex som rensevæske. 
Both in the above text and in the remaining part of the report, ”dry-cleaning shop” means a dry-cleaning shop using hydrocarbon or Rynex as cleaning fluid.
I afsnit 3 gives en kort introduktion til processerne i renserierne, herunder introduktion til de kemikalieprodukter, som anvendes i renserierne. 
In section 3, there is a short introduction to the processes in the dry-cleaning shops, including an introduction to the chemical products used.
Selve projektet består af fire faser med følgende overordnede indhold: 
The project consists of four phases with the following main contents:
· Fase 1: Udarbejdelse af bruttoliste over anvendte produkter I fase 1 blev der gennemført en spørgeskemaundersøgelse i udvalgte renserier om disses forbrug af kemiske produkter. 
· Phase 1: Creation of a gross list of the used products In phase 1, a questionnaire investigation was carried out in selected dry-cleaning shops with regard to their consumption of chemical products.