natgillin/translations-raw huggingface dataset:
På baggrund af metodeudviklingen og afprøvning på en række af de rene stoffer som anvendes i tandblegemidler, er en protokol til analyse af peroxid-indholdet i tandblegemidler opstillet: 
On the basis of the method development and the tests on the pure substances used in tooth-whitening products, a protocol for analysis of the peroxide content in tooth-whitening products was set up.
Med udgangspunkt i, at der anvendes et lukket analysekammer på ca. 100 ml i henhold til beskrivelse i afsnit 3.1, opstilles hermed følgende standardbetingelser: 
Based on the fact that the analysis uses a sealed analysis chamber of about 100 ml in accordance with the description in section 3.1, the following standard conditions can be established:
Analysen udføres ved 22 °C. 
The analysis is conducted at 22°C.
Yderligere oplysninger om produkterne, såsom forhandler, varenummer, batchnummer mv. kendes af Miljøstyrelsen. 
The Danish Environmental Protection Agency has been provided with further information about the products, (such as retailer, product no., batch no. etc.).
Parallelt med katalase-metoden, er alle produkter tillige analyseret på traditionel vis ved hjælp af redox-titreringer. 
In parallel with the catalase method, all the products were also analysed traditionally using redox titrations.
Alle produkter og de to rene stoffer, brintperoxid og ureaperoxid, er titreret med kaliumpermanganat, mens produkterne indeholdende ureaperoxid desuden er titreret med natriumthiosulfat. 
All the products and the two pure substances, hydrogen peroxide and urea peroxide, were titrated with potassium permanganate, while the products containing urea peroxide were also titrated with sodium thiosulfate.
Resultaterne fra både titreringer og test af katalase-assayet ses i Tabel 6, sammen med producentens angivelse af indholdsstoffer. 
The results of both titrations and test of the catalase bioassay are shown in Table 6, along with the manufacturers' specifications of contents.
For tre af produkterne har det ikke været muligt at få oplyst mængden af aktivstof. 
For three of the products, information on the quantity of active substance in the product was not available.
Generelt ses en fin overensstemmelse mellem koncentrationer fundet ved titrering og ved katalase assayet. 
In general, there was good correspondence between the concentrations found through titration and those found using the catalase bioassay.
Særlig lille er afvigelserne mellem tallene fra KMnO4-titreringer og katalase assayet. 
The deviations were particularly small between the concentrations found through KMnO4 titrations and the catalase bioassay.
For at afgøre, om det var en fejl ved assayet eller produktet blev endnu et sæt købt og analyseret. 
In order to determine whether this lack of peroxide content was due to a flaw in the assay or in the product, another set of products was purchased and analysed.
Denne gang blev der fundet peroxid i både ”E” og ”F” ved begge analysemetoder. 
This time around, peroxide was found in product “E” as well as “F” by both methods.
Bestemmelse af peroxid koncentrationen i de testede tandblegemidler er ved hjælp af katalase bioassayet foretaget på flere forskellige prøvekoncentrationer og i mindst 14 gentagelser per produkt. 
Determination of the peroxide concentration in the tooth-whitening products was conducted on several different sample concentrations using the catalase bioassay, and in at least 14 repetitions per product.
Tilsvarende er assayet afprøvet på de rene stoffer brintperoxid og ureaperoxid i en række forskellige koncentration. 
Correspondingly, the assay was tested on the pure substances, hydrogen peroxide and urea peroxide, in a number of different concentrations.
Variationskoefficienten på målinger af produkter med katalase bioassayet er 0,9 - 3 %. 
The coefficient of variation for measurements of products using the catalase bioassay was 0.9 - 3%.
Tilsvarende er variationen på målinger af de rene aktivstoffer 0,9 - 1,9 %. 
Correspondingly, the variation for measurements of the pure, active substances was 0.9 - 1.9%.
Redoxtitreringerne er foretaget i tre gentagelser på både produkter og rene stoffer. 
The redox titrations were conducted in repetitions of three on both products and pure substances.
For kaliumpermanganat titreringerne af tandblegeprodukterne er variationskoefficienten 0,4-2,4 %. 
For the potassium permanganate titrations of the tooth-whitening products, the coefficient of variation was 0.4 - 2.4%.
For de rene stoffer er variationen på målingerne 0,4 - 1 %. 
For the pure substances, the variation of the measurements was 0.4 - 1%.
For natriumthiosulfat titreringerne ses en meget stor variation for produkterne: 9,4 - 23,8 %. 
For the sodium thiosulfate titrations, the variation was very high for the products, namely 9.4 - 23.8%.
Dog er variationen på natriumthiosulfat titrering af ureaperoxid i ren form kun 0,33 %. 
However, the variation for sodium thiosulfate titration of urea peroxide in pure form was only 0.33%.
I forhold til de testede produkter er variationen (præcisionen) på katalase bioassayet således sammenligneligt med variationen på den kemiske analyse baseret på en kaliumpermanganat titrering, hvorimod den fremstår mere præcis end natriumthiosulfat titreringerne. 
With regard to the tested products, the variation of (accuracy of) the catalase bioassay was therefore comparable to the variation of the chemical analysis based on potassium permanganate titration, while the catalase bioassay appeared more accurate than the sodium thiosulfate titrations.
I forhold til producenternes angivelse af peroxid-indhold i produkterne afviger koncentrationsbestemmelserne foretaget med katalase bioassayet med 3,3 - 5,9 %. 
With regard to the manufacturers' specifications of the peroxide content in the products, the determinations of concentration using the catalase bioassay deviated by 3.3 - 5.9%.
Koncentrationer fundet ved kaliumpermanganat-titrering afviger 3,4 - 7,7 % og natriumthiosulfat-titrering 4,6 - 28,9 % fra producentens oplysninger. 
The concentrations found from potassium permanganate titration deviated from the manufacturers' specifications by 3.4 - 7.7% and those from sodium thiosulfate titration by 4.6 - 28.9%.
Igen er variationen på resultater fra katalase-assayet altså helt sammenligneligt med resultater fra kaliumpermanganat-titrering, og begge dele er meget bedre end natriumthiosulfat-titreringer. 
Therefore, the variability of the catalase bioassay was comparable to the variability of the potassium permanganate titration, while the variability of the sodium thiosulfate titration was higher.
Her bekræftes, at der i de testede tandblegeprodukter ikke findes stoffer der hæmmer katalase-aktiviteten. 
These confirm that the tooth-whitening products tested do not contain substances that inhibit the catalase activity.
Det udviklede katalase bioassay er altså fuldt ud brugbart til analyse af de pågældende produkter. 
Hence, the catalase bioassay developed is suitable for the analysis of tooth-whitening products.
5 Resultatvurdering og konklusion 
5 Assessment of results and conclusion
En ny metode og protokol til analyse af peroxid-indhold i tandblegeprodukter er udviklet. 
A new method and protocol for the analysis of peroxide content in tooth-whitening products was developed.
Metoden bygger på måling af iltudvikling efter enzymatisk omdannelse af peroxid til ilt og vand. 
The method is based on the measurement of changes in oxygen concentrations following enzymatic conversion of peroxide to oxygen and water.
Sammenlignet med traditionelle analysemetoder baseret på titreringer med permanganat og thiosulfat er det nyudviklede katalase bioassay nemt at udføre, og alle peroxidforbindelser - uanset om de er bundet til forskellige 'releasere' - kan måles på en gang. 
Compared to traditional analytical methods, based on titrations with permanganate and thiosulfate, the newly developed catalase bioassay is easy to conduct, and all peroxide compounds - irrespective of whether they are bound to different releasers - may be measured at once.
De fundne peroxid-indhold i tandblegeprodukterne svarer godt overens med produkt-oplysningerne. 
The peroxide contents found in the tooth-whitening products correspond well with the product specifications.
Resultaterne af metodeudviklingen og analysen af de undersøgte produkter kan kortfattet opsummeres således: 
Results of method development and product analysis can be summarised as follows:
Bestemmelse af peroxid indhold i tandblegeprodukter ved hjælp af katalase bioassayet er nemt og hurtigt at udføre 
Determination of peroxide content in tooth-whitening products through use of catalase bioassay is quick and easy.
Assayet er i stand til med stor nøjagtighed at bestemme peroxid-indholdet i produkter med meget lav koncentration af aktiv stof. 
The bioassay can determine the content of peroxides with great accuracy in products with very low concentrations of active substance.
Den nedre detektionsgrænse er 0,0002 % brintperoxid i produktet 
The lower detection limit is 0.0002% hydrogen peroxide in the product.
Til forskel fra traditionelle redox-titreringer påvirkes assayet ikke af eventuelle reducerende eller oxiderende kemikalier i produkterne 
In contrast to traditional redox titrations, the bioassay is not affected by any reducing or oxidising chemicals in the products.
Assayet kan med fordel anvendes på tandblegeprodukter med brintperoxid som aktivstof - hvad enten peroxiden findes som frit brintperoxid eller bundet i releasere 
The catalase bioassay is suitable for tooth-whitening products with hydrogen peroxide as the active substance, no matter whether the peroxide is present as free hydrogen peroxide or bound in releasers.
Assayet vil med stor sandsynlighed kunne benyttes på andre produkttyper med indhold af brintperoxid, for eksempel kosmetikprodukter hvor tilstedeværelse af fedtstoffer besværliggør redox-titreringer 
It is highly probable that the bioassay may be suitable for use on other product types containing hydrogen peroxide, e.g. cosmetics containing fat, which complicates redox titrations.
To af de testede produkter (”E” og ”F” der indkøbes som et samlet kit) viste ved gentagne analyser af samme batch ingen - eller meget lille - indhold af peroxid ved analyse med både titrering og katalase bioassay. 
In repeated analyses of the same batch, two of the products tested (”E” and ”F”, which come in a set) showed no - or a very small - content of peroxide, both using the titration method and the catalase bioassay method.
Ved indkøb af nyt batch blev fundet peroxid ved begge analysemetoder. 
Both analysis methods found peroxide when a new set was bought and tested.
Appendix to opinion on hydrogen peroxide, in its free form or when released, in oral hygiene products. 
Appendix to opinion on hydrogen peroxide, in its free state or when released, in oral hygiene products.
Bilag 1: Tekniske specifikationer for ilt-elektroden. 
Anex 1: Technical specifications of the oxygen probe.
Bilag 2: Anvendt måleudstyr 
Annex 2: Measuring equipment used
Bilag 3: Afprøvning af katalase bioassay på tandblegeprodukter. 
Annex 3: Test of the catalase bioassay on tooth-whitening products, curves
Alle produkter er analyseret som beskrevet i protokollen, og efter endt reaktion er der tilsat en kendt mængde ureaperoxid. 
All the products were analysed as described in the protocol, and a known quantity of urea peroxide was then added after completion of the reaction.
Kontrollerne bekræfter, at der i de testede tandblegeprodukter ikke findes stoffer der hæmmer katalase-aktiviteten. 
The analyses of the products confirm that there are no substances in the tooth-whitening products tested which inhibit the activity of the catalase.
Alle forløb har samme opbygning: 
The same procedure was used on each of the products:
Pil 1 angiver tilsætning af tandblegeproduktet og katalase 
Arrow 1 indicates where tooth-whitening product and catalase were added
Pil 2 angiver tilsætning af yderlige katalase 
Arrow 2 indicates where more catalase was added
Pil 3 angiver tilsætning af kendt koncentration ureaperoxid opløsning. 
Arrow 3 indicates where urea peroxide solution in a known concentration was added.
3a: Produkt ”A” 
3a: Product ”A”
Grænseværdier for motorsportsbaner 
Motorsport track noise zone
De vejledende støjgrænser er almindeligvis fastlagt ud fra undersøgelser af store befolkningsgruppers opfattelse af støjen. 
In spatial planning, the authorities designate a noise zone around motor sport tracks and other noise sources, where the noise level exceeds the recommended noise limit.
Nedenfor gives en gennemgang af grænseværdierne for motorsportsbaner. 
Below is a review of recommended noise limits for motorsport tracks.
Oversigt over den danske regulering af næringsstoffer i landbruget 
Overview of the Danish regulation of nutrients in agriculture
det danske nitrathandlingsprogram 
the Danish Nitrates Action Programme
jf. Rådets direktiv af 12. december 1991 om beskyttelse af vand mod forurening forårsaget af nitrater, der stammer fra landbruget (91/676/EØF) 
cf. Council Directive of 12 December 1991 concerning the protection of waters against pollution caused by nitrates from agricultural sources (91/676/EEC)
1.2.2 Fremtidige elementer i national lovgivning: Målrettet regulering .. 
1.2.2 Future elements in national legislation: Targeted regulation ...........
2.1 OPTIMERING AF KVÆLSTOFKREDSLØBET I LANDBRUGSPRODUKTIONSSYSTEMER 
2.1 OPTIMIZING NUTRIENT FLOWS IN AGRICULTURAL PRODUCTION SYSTEMS ........
9 2.1.3 Den reviderede fosforregulering: direkte fosforlofter på 
9 2.1.3 The revised phosphorus regulation: direct phosphorus ceilings at
3.1 MINDRE TEKNISKE JUSTERINGER I DET REVIDEREDE PROGRAM ..................... 
3.1 MINOR TECHNICAL ADJUSTMENTS IN THE REVISED PROGRAMME ................
Dette dokument beskriver både den generelle regulering af landbruget i forhold til reduktion af næringsstoftabet til vandmiljøet ved landbrugsaktiviteter og nitrathandlingsprogrammet i henhold til nitratdirektivet, som det er implementeret i nationale love og bekendtgørelser. 
This document describes both the general agricultural regulation with respect to reducing nutrient losses from agricultural activities to the aquatic environment and the actual Danish Nitrates Action Programme according to the Nitrates Directive, as it is implemented in national acts and orders.
Nitrathandlingsprogrammet præsenteres separat i kapitel 3, mens andre dele af rammerne for den danske regulering af næringsstofanvendelsen er angivet i kapitel 2 i dette dokument. 
The Nitrates Action Programme is presented separately in chapter 3, while other features of the Danish regulatory framework for nutrient management are depicted in chapter 2 in this document.
Det forrige danske nitrathandlingsprogram beskrev implementeringen af nitratdirektivet i Danmark i perioden fra 2008 til 2015. 
The previous Danish Nitrates Action Programme described the implementation of the Nitrates Directive in Denmark for the period 2008 to 2015.
Den 21. december 2015 traf Miljøstyrelsen afgørelse om, at forlænge gyldigheden af det danske nitrathandlingsprogram 2008-2015, indtil et revideret program var udarbejdet. 
On December 21, 2015, the Environmental Protection Agency announced to extend the validity of the Danish Nitrates Action Programme 2008-2015 until a revised Programme had been prepared.
Den 18. marts 2016 informerede de danske myndigheder Kommissionen om ændringen af det danske nitrathandlingsprogram i forhold til udfasningen af reduktionen af normerne for anvendelse af kvælstof. 
The Danish authorities informed the Commission on March 18, 2016 about the revision of the Danish Nitrates Action Programme, concerning the removal of the reduction of the nitrogen application standards.
Det reviderede nitrathandlingsprogram er beskrevet i kapitel 3 i nærværende dokument. 
The revised Nitrates Action Programme is described in chapter 3 of this document.
Nye og ændrede juridiske elementer, der regulerer den generelle næringsstofanvendelse i Danmark, er beskrevet nærmere i kapitel 2 i dette dokument. 
New and revised legal elements, regulating nutrient management in Denmark in general, can be found in further detail in chapter 2 of this document.
1.1 INDSATSER OG RESULTATER 
1.1 EFFORTS AND ACHIEVEMENTS
Siden slutningen af 1980'erne har Danmark haft en vidtgående og effektiv tilgang til at forbedre den miljømæssige tilstand af grundvandet og overfladevandet i forhold til nitratkoncentrationer, især med henblik på at reducere den nitratudvaskning, der er forårsaget af landbruget. 
Since the late 1980's, Denmark has pursued a comprehensive and efficient approach to improve the environmental state of groundwater and surface water regarding nitrate concentrations, especially directed towards reductions in nitrate leaching from agricultural sources.
Den første vandmiljøplan blev vedtaget i 1987 og er siden blevet fulgt op af efterfølgende handlingsprogrammer for at sikre, at der blev gjort tilstrækkelige indsatser for at reducere tabet af kvælstof og fosfor til vandmiljøet. 
The first Action Plan on the Aquatic Environment was adopted in 1987 and has since then been followed by subsequent Action Programmes to ensure that sufficient efforts were made to reduce the loss of nitrogen and phosphorus to the aquatic environment.
I 2004 blev Vandmiljøplan III vedtaget med det formål at reducere nitratudvaskningen med yderligere 13 % sammenlignet med udvaskningen af kvælstof i 2003. 
In 2004, Action Plan III for the aquatic environment was adopted, the aim being a further reduction in nitrate leaching of 13% compared to the nitrogen leaching in 2003.
Målet skulle nås i 2015. 
The target was to be obtained by 2015.
I 2008 blev der foretaget en midtvejsevaluering af Vandmiljøplan III, herunder en genberegning af nitratudvaskningen for 2003, ved hjælp af opdaterede modelleringssystemer for N-udvaskning. 
In 2008, a mid-term evaluation of Action Plan III was performed, including recalculation of the nitrate leaching for 2003 using updated N leaching modelling systems.
Evalueringen viste, at der endnu ikke var nogen væsentlig reduktion i den modellerede nitratudvaskning fra 2003-2007, og at det var usandsynligt, at målsætningen i Vandmiljøplan III kunne indfries fuldstændigt i 2015. 
The evaluation showed that there was not yet any significant decrease in the modelled nitrate leaching during 2003-2007 and that it was unlikely that the aim in AP III would be fully attained by 2015.
Som en konsekvens heraf blev Vandmiljøplan III erstattet af Aftale om Grøn Vækst i juni 2009. 
As a consequence, the AP III was replaced by the Green Growth Agreement in June 2009.
Denne plan omfattede et nyt koncept for definitionen af målet for regulering af næringsstoffer. 
This plan included a new concept for defining the aim of nutrient regulation.
De tidligere handlingsplaner indeholdt mål for reduktionen af udvaskningen af kvælstof fra rodzonevand, mens målet med Aftale om Grøn Vækst var at reducere den årlige belastning af kvælstof i åbne kystvande yderligere. 
The previous Action Plans provided goals for the reduction of nitrogen leaching from the root zone water, whereas the aim of the Green Growth Agreement was to further reduce the annual load of nitrogen to marine waters.
N-belastningen i åbne kystvande er gradvist blevet reduceret, efterhånden som de planlagte foranstaltninger for punktkilder og landbruget er blevet implementeret. 
The N load to marine waters has stepwise been reduced, as planned measures for point sources and agriculture has been implemented.
Den anden udgave af 
The second generation of River
vandområdeplanerne for 2015-2021 blev færdiggjort i juni 2016. 
Basin Management Plans for 2015-2021 have been finalized in June 2016.
1.2 DEN POLITISKE AFTALE OM FØDEVARER OG LANDBRUG 
1.2 THE POLITICAL AGREEMENT ON FOOD AND AGRICULTURE
Den 22. december 2015 indgik regeringen og dens støttepartier Aftale om Fødevare- og landbrugspakke. 
On 22 December 2015, the Danish government and supporting political parties in the Danish Parliament reached an agreement on a Food and Agricultural Package.
Aftalen omfatter en pakke med forskellige foranstaltninger, der ændrer den måde, hvorpå den miljømæssige regulering af landbrugssektoren udføres: fra en generel regulering til en mere målrettet tilgang. 
The agreement includes a diverse package of measures, initiating a shift in the way environmental regulation of the agricultural sector is carried out: from a general regulation to a more targeted approach.
Formålet er at forbedre fødevare- og landbrugserhvervets mulighed for at øge den primære produktion og eksporten, styrke konkurrenceevnen - i det rette samspil med beskyttelsen af natur og miljø. 
The aim is to improve the ability of the food and agricultural industry to increase primary production and exports, ensure a more level playing field - in due interaction with the protection of nature and the environment.
1.2.1 Elementer, implementeret i national lovgivning Et centralt element i aftalen er at udfase reduktionen i kvælstofnormerne, som førhen var blevet reduceret med ca. 20 % sammenlignet med det økonomisk optimale niveau. 
1.2.1 Elements, implemented in national legislation One central element in the agreement is to remove the reduction of nitrogen application standards for farming, which have been reduced by approximately 20% compared to the economically optimal level.
Udfasningen af reduktionen af kvælstofnormerne er sker gradvist ved at fjerne to tredjedele i foråret 2016 med virkning fra afgrødesæsonen 2015/16, og ved at fjerne den resterende tredjedel med virkning fra afgrødesæsonen 2016/17 og fremefter. 
The removal of the reduction of the nitrogen application standards takes place stepwise by removing two thirds in spring 2016, coming into effect during the crop season 2015/16 and by removing the remaining one third with effect from the crop season 2016/17 and onwards.
Denne ændring i reguleringen forudsatte en ændring af det danske nitrathandlingsprogram. 
This change in regulation presupposes a revision of the Danish Nitrates Action Programme.
For at undgå en øgning i nitratudvaskningen som følge af denne justering er der fastsat afværgende foranstaltninger i 2017, som består af følgende: 
In order to avoid an increase in nitrate leaching due to this adjustment, measures to avert have been established in 2017, consisting of the following:
• Ændringer i reguleringen af fastsættelsen af obligatoriske efterafgrøder og 
• Changes in regulation of establishment of mandatory catch crops and use of
• Yderligere etablering af (mini-)vådområder (se kapitlerne 2.4.1 og 2.4.2) 
• Additional establishment of (mini-)wetlands (see chapters 2.4.1 & 2.4.2)
• Skovrejsning (se kapitel 2.4.4) 
• Afforestation(see chapter 2.4.4)
• Målrettet ordning for efterafgrøder (se kapitel 2.4.8) 
• Targeted catch crop scheme (see chapter 2.4.8)
Derudover fremlægger regeringen en ny og mere emissionsbaseret regulering af husdyrbrug i forbindelse med godkendelser. 
Furthermore, the Danish government proposes a new and more emission based regulation of livestock holdings when granting permits to installations for animal husbandry.
Reguleringen sikrer en mere enkel og fleksibel regulering, der er udformet som en godkendelse baseret på en miljømæssig vurdering af produktionsarealet i stalden og sikring af en generel regulering af udbringning af husdyrgødning. 
The regulation ensures a simpler and flexible regulation designed as a permit based on an environmental assessment of the production area in the stable, and ensure general regulation of the spreading of the manure.
Denne regulering er beskrevet nærmere i afsnit 2.2. 
This regulation is described in further detail in section 2.2.
Med virkning fra 2017 justerer regeringen de såkaldte harmoniregler, der begrænser mængden af kvælstof fra husdyrgødning pr. hektar for at sikre, at kravet er på linje med kravet i nitratdirektivet. 
Coming into effect from 2017, the Danish government adjusts the so-called harmony rules” limiting the amount of nitrates from livestock manure per hectare, to ensure that the requirement is aligned with the requirement of the Nitrates Directive.