Vejledning om strandrensning - Naturstyrelsen

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Kapitel 9 indeholder en beskrivelse af forskelligt materiel til anvendelse ved rensning af kyster. Der er i kapitlet dels gennemgået hvilket specialudstyr, der kan anvendes, ligesom det er gennemgået, hvorledes almindeligt entreprenørmateriel kan anvendes. Ud over at olien udgør en fare for miljøet, er der arbejdssikkerhedsmæssige og sundhedsmæssige forholdsregler, der må iagttages for at undgå at de personer, der deltager i rensningsarbejdet og håndterer den opsamlede olie, pådrager sig skader eller sygdomme. Der er derfor i vejledningen medtaget et særligt kapitel om arbejdssikkerhed og sundhedsfare i forbindelse med oprensning af visse typer af olieprodukter (kapitel 11). Identifikation af forureneren og bevisførelse i en erstatnings/straffesag er et emne, der i de senere år har været genstand for megen opmærksomhed, ligesom en betragtelig udvikling har fundet sted indenfor dette område. Disse forhold afspejles i det reviderede kapitel 10 om prøvetagning. Uanset at vejledningen alene omhandler bekæmpelse af forureninger forårsaget af olie, giver kapitel 14 en kort beskrivelse af, hvorledes der bør forholdes i tilfælde af ilanddrevne tromler, beholdere, kasser og lignende strandingsgods.
Summary The Danish Environmental Protection Agency has prepared the present updated guideline for cleaning of oil contaminated beaches and other coastal areas. The main target group for this guideline is local municipalities holding responsibility for coastal cleaning in case of oil contamination of coastal areas. In chapter 2 of the present guideline, the general delegation of responsibility in case of pollution of the sea, of coasts, beaches and harbours is described. Chapter 3 gives a number of guidelines for municipal contingency plans for remediation of coasts, beaches and harbours after oil pollution. Chapter 4 describes the rules laid down concerning distribution of expenses for emergency preparedness and control measures between the authorities involved. Chapter 5 gives a short description of some of the most important oil pollution incidents during the last 35 years. The chapter exemplifies different cleaning actions and effects of oil contamination. This will give an insight in the diversity of oil contamination and illustrate the experiences from previous oil contamination e.g. the importance of alert plans. Chapters 6-13 include descriptions of different beach cleaning methods used for certain stretches of coast in relation to the stretches’ geologic shape, biological vulnerability and the size and type of the oil spill etc. The aim of the guidelines is to point out beach cleaning methods that pay as much attention as possible to the vulnerability of the different coast types to oil pollution and the cleaning work. Previous oil pollution incidents have shown that the character of the pollution and consequently the most effectual cleaning methods vary from incident to incident. As this makes it impossible to draw up detailed guidelines for cleaning work covering any conceivable oil pollution incident at a stretch of coast, an assessment must be made for each oil pollution incident stating which cleaning and disposal methods will be most suitable. To support this assessment, the physical properties of significance for spreading and transformation of different oil types on the beach, are reviewed in chapter 6. This is further detailed in chapter 7, where it is described, how it must be expected that spilled oil will be degraded and spread after spills at sea. Biological impacts of oil pollution are outlined in chapter 8. The background for this is that knowledge of the potential biological harmful effects influences how the cleaning must be approached, and which coast lines must given priority to protection against the spilled oil. The clean up of the different coast types are described in chapter 12. Moreover this chapter includes a description of how it can be prioritised which coast lines should be protected first in case of threatening oil pollution and which coast lines should be given high priority regarding cleaning after an oil pollution has occurred. The chapter also includes a more detailed review of cleaning methods for different coast types, and it is described how after-cleaning could be accomplished.
Page 1 and 2: Vejledning om strandrensning Juli 2
Page 3 and 4: 6.1.2. Databaser over oliers egensk
Page 5 and 6: 12.2. OLIENS SPREDNING OG KYSTERNES
Page 7: Sammenfatning Vejledningen gennemg
Page 11 and 12: 1. Indledning Denne vejledning om s
Page 13 and 14: 2.2. Rapportering af observeret for
Page 15 and 16: 2.5. Indsatsens afslutning Det påh
Page 17 and 18: 3) Oversigt over kontaktmuligheder
Page 19 and 20: 7. Foranledige prøver af indsamlet
Page 21 and 22: Det skal bemærkes, at anvendelse a
Page 23 and 24: Udgifter til bekæmpelse af olie- o
Page 25 and 26: det åbne hav, og olien drev mod M
Page 27 and 28: truede amter og kommuner. Disse pla
Page 29 and 30: Tabel 1 Overordnet inddeling af oli
Page 31 and 32: 6.2. Eksempler på råolier og olie
Page 33 and 34: 6.2.2.2. Væskeformige og faste kul
Page 35 and 36: 6.3. Nogle fysiske egenskaber Olien
Page 37 and 38: API-skalaen er baseret på vand, hv
Page 39 and 40: 7. Spredning og omdannelse af olie
Page 41 and 42: Efter den første fordampning af de
Page 43 and 44: 0,5 procent. Det kan betyde, at oli
Page 45 and 46: 8. Biologiske skadevirkninger Råol
Page 47 and 48: koncentrationer kan således for de
Page 49 and 50: 9. Materiel I den udstrækning komm
Page 51 and 52: Figur 3:, Spærring til at hindre o
Page 53 and 54: hensyn til udskiftningen af spærri
Page 55 and 56: Figur 9: Opbygning af spærring, de
Page 57 and 58: Figur 12: Princippet i en skiveskim
Page 59 and 60:
Figur 16: Olietrawl, trawlposen med
Page 61 and 62:
Dispergeringsmidlers effekt på en
Page 63 and 64:
9.6. Rensning af materiel Figur 18:
Page 65 and 66:
10. Prøvetagning Dette kapitel er
Page 67 and 68:
en skovl, en øse, eller anden form
Page 69 and 70:
2. Dato og klokkeslæt for prøveta
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Foretag “skumningen” flere gang
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10.14.2. Remote Sensing (fjernoverv
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man selv og andre er placeret såle
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Der findes to hovedtyper åndedræt
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Det tilsmudsede tøj og udstyr læg
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min). Der kan være behov for yderl
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12. Rensning af olieforurenede kyst
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) døde fugle og fisk. c) drivtømm
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12.2. Oliens spredning og kysternes
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Hvis der er kendskab til et olieuds
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Følsomheds-indeks - ESI 1 2 Tabel
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Tabel 9: Vurdering af faren for rem
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Uanset prioriteringen, kan andre he
Page 97 and 98:
Tabel 11: Sårbarhedstabel for natu
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ensningsarbejde forestår, når ise
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Større olieklumper kan rives samme
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Olie, der er koncentreret i vandkan
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Strandengene oversvømmes hyppigst
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suppleres med endnu er spærring, d
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Spuling, optagning med slamsuger og
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Det kan i nogle tilfælde være van
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13. Fremme af den biologiske nedbry
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egravet i bundmaterialet eller på
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yderligere kvælstof. Undersøgelse
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I Tabel 13 er der en sammenfatning
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olien ved denne behandling føres l
Page 123 and 124:
14. Ilanddrevne tromler m.v. 14.1.
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Vejledning om strandrensning - Naturstyrelsen

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