natgillin/translations-raw huggingface dataset:
I mængden indgår forbrændingsskrot. 
Incineration scraps are included in the quantity.
Produktionen af nyt papir på de danske papirfabrikker blev 269.600 tons. 
The production of new paper in the Danish paper mills was 269.600 tons.
Genanvendelsen af returpapir er opgjort til 888.600 tons, hvilket svarer til 61,3 procent af potentialet. 
The recycling of recycled paper has been assessed to 888.600 tons, which corresponds to 61.3 per cent of the potential.
Hovedparten (69 procent) af forbruget bestod af PE (polyethylen). 
The main part (69 per cent) of the consumption consisted of PE (polyethylene).
Genanvendelsen af plastemballage blev beregnet til 38.700 tons, som næsten udelukkende blev indsamlet fra erhvervsvirksomhederne. 
The recycling of plastic packaging was assessed to 38.700 tons, which was almost exclusively collected from the business enterprises.
Genanvendelsesmængden svarer til 20,3 procent af potentialet. 
The recycling quantity corresponds to 20.3 per cent of the potential.
Eksporten af plastemballageaffald udgjorde 75 procent af den indsamlede mængde. 
The export of plastic packaging waste amounted to 75 per cent of the collected quantity.
Hovedparten af træemballage består af træpaller. 
The main part of wood packaging consists of wood pallets.
I 2006 blev der indsamlet og repareret ca. 1,8 mio. træpaller. 
In 2006 approx. 1.8 million wood pallets were being collected and repaired.
Den genanvendte mængde er beregnet til 36.100 tons, hvilket giver en genanvendelsesprocent på 34. 
The recycled quantity has been assessed to 36.100 tons, which gives a recycling percentage of 34.
Den samlede forsyning af de fem emballagematerialer (der udgør 99,5 % af al emballage) er beregnet til 974.500 tons i 2006. 
The total supply of the five packaging materials (which amounts to 99.5 per cent of all packaging) has been assessed to 974.500 tons in 2006.
Heraf blev der indsamlet 545.500 tons til genanvendelse eller 56,0 procent af al emballage. 
Of this, 545.500 tons were being collected for recycling or 56.0 per cent of all packaging.
EU kommissionens mål er minimum 55 procent i 2008. 
EU's target is minimum 55 per cent in 2008.
Mængden af indsamlet glasemballage er uændret - men forbruget falder 
The quantity of collected glass packaging is unchanged - however, the consumption decreases
I 2006 blev der anvendt 143.385 tons glasemballage. 
In 2006, 143.385 tons glass packaging was used.
Mængden af emballage i retursystemer indgår ikke heri. 
The quantity of packaging in the recycling systems is not included in this.
I forhold til 2005 er der tale om et fald i forbruget. 
Compared with 2005, a decrease has taken place in the consumption.
I 2006 blev der indsamlet 101,4 millioner hele flasker, hvilket svarer til ca. 45.650 tons (Tabel 1). 
In 2006 approx. 101.4 million unbroken bottles were collected, which corresponds to approx. 45.650 tons (Table 1).
Af denne flaskemængde blev 11.642 tons genpåfyldt i Danmark, mens resten blev eksporteret. 
Out of this bottle quantity, 11.642 tons were refilled in Denmark, while the remaining was exported.
Den relative høje eksportandel er et udtryk for at tapperierne i Danmark ikke har mulighed for at aftage større mængder, end tilfældet er i dag. 
The relatively high export part is a result of the fact that the bottleries in Denmark have no possibility to purchase larger quantities than what is the case today.
En af grundene er, at mængden af importeret bulkvin, der typisk tappes på genbrugsflasker, er relativ lille, svarende til 40 procent af forbruget. 
One of the reasons is that the quantity of imported bulk wine, which is typically bottled on recycled bottles, is relatively small corresponding to 40 per cent of the consumption.
Anm.: Statistikken medtager ikke emballage i retursystemer 
Note: The statistics do not include packaging in recycling systems
1) Privates køb i grænsehandel 
1) Private persons' purchases in border trade
3) Inklusive indsamlede deponerede skår 
3) Including collected deposited broken glass
Resten af den indsamlede glasemballage i 2006, nemlig 74.892 tons, bestod fortrinsvis af skår til genanvendelse (Tabel 1). 
The remaining part of the collected glass packaging in 2006, i.e. 74.892 tons, primarily consisted of broken glass for recycling (Table 1).
Af mængden blev 43.241 tons genanvendt i Danmark og resten eksporteret. 
Of this quantity, 43.241 tons were being recycled in Denmark and the remaining part was exported.
Bryggeriskår er ikke medregnet. 
Brewery broken glass is not included.
Mængden af indsamlet metalemballage er steget i 2006 
The quantity of collected metal packaging increased in 2006
Det samlede potentiale er for 2006 beregnet til 42.375 tons. 
The collected potential for 2006 has been estimated to 42.375 tons.
Der blev indsamlet 26.137 tons metalemballage til genanvendelse i 2006, hvilket svarer til 61,6 procent af det samlede potentiale. 
26.137 tons of metal packaging was being collected for recycling in 2006, which corresponds to 61.6 per cent of the total potential.
Der er således tale om en stigning i forhold til 2005, hvor der blev indsamlet 23.917 tons. 
An increase has taken place compared to 2005, where 23.917 tons were being collected.
Stigningen skyldes en stigning i mængden af såvel stål- som aluminiumsemballagen. 
The increase is due to an increase in the quantity of both the steel and the aluminium packaging.
Metalemballageforbrug og indsamling i Danmark. 
Metal packaging consumption and collection in Denmark.
Metal indsamlet via vore containerpladser bidrager med 60 procent og forbrændingsjern med 20 procent af indsamlingsmængden. 
Metal collected via our container stations contributes with 60 per cent and incineration iron with 20 per cent of the collection quantity.
Resten er indsamlet direkte fra virksomhederne. 
The remaining part is collected directly from the enterprises.
Forbruget af nyt papir steg i 2006 til i alt 1.450.450 tons (Tabel 3). 
The consumption of new paper increased in 2006 to a total of 1.450.450 tons (Table 3).
Indsamlingen af returpapir til genanvendelse blev på 888.585 tons. 
The collection of recycled paper for recycling amounted to 888.585 tons.
I forhold til forbruget, blev 61,3 procent af papiret genanvendt. 
Compared with the consumption, 61.3 per cent of paper was being recycled.
Handel og kontor samt private husholdninger bidrog tilsammen med 75 procent af indsamlingsmængden. 
Trade and offices together with private households contributed as a whole with 75 per cent of the collection quantity.
Forbrug, indsamling og genanvendelse af papir i Danmark. 
Consumption, collection and recycling of paper in Denmark.
Hvordan beregnes papir- og papemballagemængden 
Increase in collection of plastic packaging
Forbruget af træemballage er opgjort til 106.436 tons i 2006. 
The consumption of wood packaging has been assessed to 106.436 tons in 2006.
Derudover findes der en mængde pakkasser, tremmekasser og trætromler. 
In addition there is a quantity of cardboard boxes, crates and wood drums.
Opgørelsen af den indsamlede og genanvendelige mængde tager afsæt i en beregning af antallet af EUR paller, der tages ud af retursystemet med henblik på reparation. 
The specification of the collected and recyclable quantity is based on an estimation of the number of EUR pallets, which are removed from the recycling system in order to be repaired.
Efter reparation indgår disse igen retursystemet. 
After repair, these pallets are again included in the recycling system.
I 2006 blev der indsamlet 2,9 mio. paller til reparation, hvoraf knapt 25 procent kasseres. 
In 2006, 2.9 million pallets were collected for repair, out of which 25 per cent is being discarded.
Afhængig af pallestørrelse udskiftes der mellem 2 og 4 kg i gennemsnit per EUR-palle. 
Dependent upon the pallet size, between 2 and 4 kilos in average per EUR pallet is being replaced.
Med denne forudsætning er den genanvendelige mængde beregnet til 36.091 tons. 
With this assumption, the recyclable quantity has been assessed to 36.091 tons.
I forhold til det samlede træemballageforbrug udgør den genanvendelige mængde 34 procent i 2006. 
Compared to the total wood packaging consumption, the recycable quantity amounts to 34 per cent in 2006.
Indberetning til EU 
Reporting to EU
I henhold til EU's emballagedirektiv skal Danmark årligt indberette oplysninger om, hvorledes indsamlingen og genanvendelsen af de fem emballagematerialer udvikler sig i forhold til de konkretiserede mål. 
According to EU's Packaging Directive, Denmark must each year report information about how the collection and recycling of the five packaging materials develop compared with the specific targets.
De opnåede resultater og de respektive mål fremgår af Tabel 6. 
The achieved results and the respective targets are shown in Table 6.
Der gøres opmærksom på, at opgørelsen af glasemballageforbruget og genanvendelsen af glasemballage til EU kommissionen baserer sig på andre forudsætninger end dem, der er anvendt i Tabel 1. 
Please note that the calculated glass packaging consumption and the recycling of glass packaging reported to the EU Commission is based on other assumptions that those being used in Table 1.
Det indebærer, at de to talsæt i henholdsvis Tabel 1 og Tabel 6 ikke er identiske. 
This implies that the two sets of figures in respectively Table 1 and Table 6 are not identical.
Feminisering af hanfisk i ferskvandsmiljøet og det marine vandmiljø 
Feminisation of male fish in freshwater and marine environments
Gennem de seneste ti år har man fundet feminisering af hanfisk i en række europæiske lande samt i USA og Japan ( 1-12 ). 
During the past ten years feminisation of male fish has been detected in several European countries and in USA and Japan ( 1-12 ).
Disse tilfælde er eksempler på forstyrrelser af det hanlige forplantningssystem, som menes at være en konsekvens af hormonforstyrrelser forårsaget af hunlige hormoner, østrogener, eller østrogenlignende kemikalier, som er til stede i det akvatiske miljø. 
These cases are examples of disturbances of the male reproductive system which are believed to be consequences of endocrine disruption caused by female hormones, estrogens, or chemicals mimicking estrogens present in the aquatic environment.
Størstedelen af østrogenerne formodes at nå det vandige miljø med spildevandsudledninger. 
The majority of estrogens are believed to reach the aquatic environment by sewage effluent.
I Europa er feminisering af hanfisk udsat for spildevand set i England ( 1 ), Sverige ( 3 ), Norge ( 4 ), Tyskland ( 5 ), Holland ( 6 ), Frankrig ( 7 ; 13 ), Spanien ( 8 ; 14 ) og Danmark ( 2 ). 
In Europe feminisation of male fish exposed to sewage effluent has been seen in England ( 1 ), Sweden ( 3 ), Norway ( 4 ), Germany ( 5 ), The Netherlands ( 6 ), France ( 7 ; 13 ), Spain ( 8 ; 14 ) and Denmark ( 2 ).
Desuden har man gjort observationerne af feminisering blandt vildtlevende fiskebestande hos flere arter incl. ferskvandsarterne skalle ( 1 ), grundling ( 15 ), karpe ( 8 ; 14 ), brasen ( 5 ; 6 ), døbel ( 7 ; 13 ) og bækørred ( 2 ) samt saltvandsarterne skrubbe ( 16-22 ), ålekvabbe ( 18 ) og to arter af sandkutling ( 23 ). 
Further, the observations of feminisation in wild populations of fish have been made in a range of different species including the freshwater species roach ( 1 ), gudgeon ( 15 ), carp ( 8 ; 14 ), bream ( 5 ; 6 ), chub ( 7 ; 13 ) and brown trout ( 2 ) and the saltwater species flounder( 16-22 ), eelpout ( 18 ) and two species of sand gobies ( 23 ).
Disse typer af forstyrrelser i det hanlige forplantningssystem er således både blevet fundet i det ferske og marine vandmiljø, skønt de fleste tilfælde er blevet rapporteret fra ferskvandsmiljøet. 
Thus, these kinds of disruption of the male reproductive system have both been found in freshwater and marine environments though most cases have been reported from freshwater environments.
Kontrollerede eksponeringer af fisk for spildevand i f.eks. burforsøg har yderligere givet evidens for den østrogene aktivitet i spildevand og østrogener og/eller østrogene stoffer som årsag til forstyrrelserne. 
Controlled exposure of fish to sewage effluent i.e. in cage experiments have further added proof to the estrogenic nature of the sewage effluent and estrogens or estrogenic chemicals as causative agents of the disruptions.
Tegnene på feminisering i hanfisk er dannelsen af et hunligt blommeprotein, som kun dannes som respons på en østrogen påvirkning, samt forekomsten af intersex en unormal form for tvekønnethed. 
The signs of feminisation in male fish are the production of a female yolk protein which is known only to be produced as a response to an estrogen exposure, and the occurrence of intersex an abnormal form of hermaphroditism.
Hanner, der udviser intersex, har tidlige stadier af ægceller i testiklerne, og i nogle tilfælde har de også udviklet den hunlige struktur, som leder æggene til æggelederen. 
Males with the intersex condition have early stages of egg cells in the testis and in some cases they have also developed the female duct which leads eggs to the oviduct.
Feminisering er blevet fundet i forskellige udviklingsgrader blandt fisk fra milde til alvorlige forstyrrelser af det hanlige forplantningssystem. 
Feminisation has been found in varying degrees among individual fish from mild to very severe disturbances of the male reproductive system.
Den feminisering af fisk, som er blevet fundet i Danmark afviger dog ikke markant fra det omfang, der er set i de øvrige lande uden for England. 
In these a lower occurrence and severity of feminisation compared to England have generally been seen though feminisation has been detected at several of the examined sites.
I alle lande, hvor undersøgelser er foretaget, er der fundet lokaliteter, hvor fiskepopulationer er upåvirkede. 
There are, however, also sites where the fish populations appear unaffected.
Det skal pointeres, at korttids-eksponeringsforsøg, hvor fisk kun udsættes for spildevand for en kort periode, ikke altid giver et korrekt estimat af risikoen for vilde populationer af fisk, som lever hele deres liv i det pågældende vandløb. 
It should be pointed out that short-term exposure experiments, where fish are exposed to sewage effluent for a short period of time, do not always give a correct estimate of the risk for wild populations of fish which live their entire life in the stream or river.
Det er påvist, at en øget eksponeringstid for spildevand nedsætter den koncentration af spildevand, som kræves for at forårsage feminisering af fisk ( 24 ). 
It has been demonstrated that increasing the exposure time for sewage effluent lowers the concentration of sewage effluent needed to cause feminisation of fish ( 24 ).
Østrogenicitet af spildevand 
Estrogenicity of sewage effluent
Teorien om, at østrogener/østrogene stoffer i spildevand er årsag til feminiseringen af hanfisk, støttes også af en række forsøg, hvor der er anvendt cellekultur-testsystemer udviklet til at detektere østrogen aktivitet. 
Support to the theory of estrogenic compounds in sewage effluent as the cause of the feminising effects, which have been found among male fish, has also come from a number of studies using cell culture assays designed to detect estrogenic activity.
Når ethinyløstradiol detekteres, er det oftest under 10 ng/l. De koncentrationer, der er målt i dansk spildevand ligger indenfor de østrogenkoncentrationer, som er rapporteret fra andre europæiske lande. 
When ethinylestradiol is detected it is mostly below 10 ng/l. The concentrations measured in Danish sewage effluent lie within the typical range of estrogen concentrations reported from other Europeans countries.
I overfladevand er østrogenkoncentrationerne lavere end i spildevand og er detekteret i intervallerne 0,05 15,5 ng østradiol/l, < 0,1 17 ng østron/l, < 0,1 3,4 ng østriol/l and < 0,053 30,8 ng ethinyløstradiol/l med typiske koncentrationer under 5 ng/l for østradiol og østron og mindre end 1 ng/l for ethinyløstradiol. 
In surface waters, concentrations of estrogens are lower compared to sewage effluent and have been detected at concentrations of 0.05 15.5 ng estradiol/l, < 0.1 17 ng estrone/l, < 0.1 3.4 ng estriol/l and < 0.053 30.8 ng ethinylestradiol/l with typical concentrations of less than 5 ng/l for estradiol and estrone and less than 1 ng/l for ethinylestradiol.
I både spildevand og overfladevand er østron det hyppigst forekommende og ethinyløstradiol det sjældnest forekommende af østrogenerne. 
For both sewage and surface water estrone is the most and ethinylestradiol the least frequently detected estrogen.
En vigtig ting, man skal være opmærksom på, når der nævnes østrogenkoncentrationer i nærværende rapport, er, at det sjældent er specificeret, hvorvidt de kemiske analyser kun måler frie eller både frie og konjugerede østrogener. 
An important thing which has to be remembered whenever concentrations of estrogens are mentioned in the present report is, however, that it seldom is specified whether the chemical analysis measures only free or both free and conjugated estrogens.
Man må også formode, at der er større usikkerheder forbundet med østrogenmålinger i indløbs- end udløbsspildevand primært pga. interferens fra store mængder organisk stof (matrix effekt). 
There must probably also be expected to be larger uncertainties related to measurements of estrogen concentrations in influent than in effluent due primarily to interference from large contents of organic matter (matrix effect).
Desuden er detektionsgrænsen for analyserne især for ethinylestradiol tæt på og nogle gange endda over de koncentrationer, man har vist kan forårsage kønsforstyrrelser hos fisk. 
Further, the detection limits of the analyses, especially for ethinylestradiol, are close to and sometimes even above the concentrations which have been demonstrated to cause reproductive disturbances in fish.
Østrogeners skæbne i det vandige miljø 
Fate of estrogens in the aquatic environment
Vor viden om østrogeners skæbne, adfærd og persistens i miljøet er stadig relativt begrænset. 
Knowledge on the fate, behaviour and persistence of estrogens in the environment is still relatively limited.
Det syntetiske ethinyløstradiol er dog tilsyneladende mere persistent end de naturlige østrogener både i vandfasen og i sediment. 
The synthetic ethinylestradiol seems, however, to be more persistent than the natural estrogens both in water and sediment.
Forkomst og skæbne af udvalgte østrogene stoffer i spildevand og overfladevand 
Occurrence and fate of selected estrogenic compounds in sewage effluent and surface water
Alkylphenoler og bisphenol A hører til de mere potente af de østrogene kemikalier, som kan frigives med spildevand, og som derfor er omtalt i denne rapport. 
Alkylphenols and bisphenol A are two of the more potent of the estrogenic chemicals which might be released with sewage effluent and which therefore receive some attention in the present report.
De vigtigste alkylphenoler mht. østrogenicitet er nonylphenol og oktylphenol. 
The most important alkylphenols with regard to estrogenicity are nonylphenol and octylphenol.
Bisphenol A er mindre hyppigt forekommende og er sjældent målt i koncentrationer over 1 µg/l i spildevand og overfladevand. 
Bisphenol A is less frequently encountered than alkylphenols and has seldom been detected at concentrations above 1 µg/l in either sewage effluent or surface water.
Som for østrogener fordeler alkylphenoler og bisphenol A sig mellem vandfasen og sedimentet, og der er indikationer for, at begge har et stort potentiale for at akkumulere i sediment med ringe iltforhold ( 38 ; 39 ). 
As for estrogens, alkylphenols and bisphenol A will partition between the water phase and the sediment, and indications exist that both have a great potential for accumulating in sediment with anoxic conditions ( 38 ; 39 ).
Østrogeners, alkylphenolers og bisphenol As feminiseringspotentiale 
The feminising potential of estrogens, alkylphenols and bisphenol A
I lyset af de hormonforstyrrelser, som er observeret blandt fiskepopulationer, som har været udsat for spildevandspåvirkning, er der blevet udført et antal kontrollerede eksponeringsforsøg for at fastsætte de laveste koncentrationer af østrogener og østrogene kemikalier, som kræves for at fremkalde disse forstyrrelser. 
In light of the observations of reproductive disturbances in fish populations exposed to sewage effluent, a number of controlled exposure experiments have been performed to assess the lowest concentration of estrogens and estrogenic chemicals needed to obtain these observed disturbances.
Dette er en hjælp til at fastslå hvilke stoffer, der kan være ansvarlige for de observerede effekter som dannelse af blommeprotein hos hanner, udvikling af intersex og andre forstyrrelser af hanners testikeludvikling. 
This aids in assessing which compounds might be responsible for the observed effects such as production of yolk protein in males, development of intersex or other disturbances in the male testis.
Eksempler på andre testikeleffekter er hæmning af den normale udvikling af hanlige kønsceller, som kan ses som en lavere testikelvægt i forhold til kropsvægten og/eller en tilstedeværelse af en større andel af tidlige, mindre modne stadier af kønsceller ( 44 ). 
Examples of other effects are inhibition of the normal development of male germ cells, which can be seen as a lower relative weight of the testis and/or a presence of a larger proportion of early stages of germ cells ( 44 ).
Forekomst af nedbrudte kønsceller er også set ( 44 ). 
The presence of degenerated germ cells has also been seen ( 44 ).
En lignende men lidt lavere østrogen aktivitet er set for østron. 
A similar or slightly lower estrogenic activity has been detected for estrone.
Østriol er det mindst østrogene af de tre naturlige østrogener. 
Estriol is the least estrogenic of the three natural estradiols.
Generelt er der begrænset viden om den østrogene kapacitet af dette østrogen. 
In general, knowledge on the estrogenic capacity of this estrogen is limited.
Ethinyløstradiol er mere potent end de naturlige østrogener mht. at forårsage forstyrrelser i det hanlige forplantningssystem. 
Ethinylestradiol is even more potent than the natural estrogens in regard to inducing disruptions in the male reproductive system.
Dannelse af blommeprotein og udvikling af intersex er set ved 0,1 ng/l ( 42 ) og ændret kønsratio ved 0,6 ng/l ( 48 ). 
Induction of yolk protein and induction of intersex have been seen at 0.1 ng/l ( 42 ) and changed sex ratio at 0.6 ng/l ( 48 ).
En række andre effekter på forplantningssystemet som hæmning af den normale sædcelleudvikling er set ved koncentrationer under 10 ng/l. 
A range of other reproductive effects such as inhibition of normal sperm cell development has been seen at concentrations below 10 ng/l.
Både alkylphenolerne, nonylphenol samt oktylphenol og bisphenol A har svagere østrogen aktivitet end både naturlige og syntetiske østrogener. 
Both the alkylphenols, nonylphenol and octylphenol, and bisphenol A have a lower potency than both natural and synthetic estrogens.
Effekter er set ved koncentrationer i µg/l-området. 
Effects are seen in the µg/l concentration range.
Dannelse af blommeprotein i hanfisk er set ved en koncentration på 5 µg/l nonylphenol eller oktylphenol ( 49 ; 50 ), skønt langtidseksponering for nonylphenol sænkede den laveste effekt koncentration til 1 µg/l ( 51 ; 52 ) . 
Induction of yolk protein has been detected at 5 µg/l nonylphenol or octylphenol ( 49 ; 50 ), though at long exposure time with nonylphenol, the lowest effect concentration was decreased to 1 µg/l ( 51 ; 52 ).
Intersex, ændret kønsratio, nedbrudt testikelvæv og hæmmet vækst af testikler er set ved nonylphenol koncentrationer mellem 30 og 100 µg/l ( 50 ; 53 ; 54 ). 
Intersex, changed sex ratio, degenerated testes and inhibited growth of the testes have been seen at nonylphenol concentrations between 30 and 100 µg/l ( 50 ; 53 ; 54 ).
Koncentrationer ned til 2 µg/l oktylphenol har forårsaget forstyrrelser hos hanfisk ( 49 ). 
Concentrations down to 2 µg/l octylphenol have caused reproductive disorders in male fish ( 49 ).
Bisphenol A har udvist effekter ved koncentrationer mellem 10 og 40 µg/l ( 42 ; 55 ; 56 ). 
Bisphenol A has been demonstrated to exert effects at concentrations between 10 and 40 µg/l ( 42 ; 55 ; 56 ).