ASTM F2205-2002(2007) Standard Guide for Ecological Considerations for the Use of Chemical Dispersants in Oil Spill Response Tropical Environments《鉴于生态原因的考虑、漏油效应中的化学分散剂使用的标准指南》.pdf

《ASTM F2205-2002(2007) Standard Guide for Ecological Considerations for the Use of Chemical Dispersants in Oil Spill Response Tropical Environments《鉴于生态原因的考虑、漏油效应中的化学分散剂使用的标准指南》.pdf》由会员分享，可在线阅读，更多相关《ASTM F2205-2002(2007) Standard Guide for Ecological Considerations for the Use of Chemical Dispersants in Oil Spill Response Tropical Environments《鉴于生态原因的考虑、漏油效应中的化学分散剂使用的标准指南》.pdf（6页珍藏版）》请在麦多课文档分享上搜索。

1、Designation: F 2205 02 (Reapproved 2007)Standard Guide forEcological Considerations for the Use of ChemicalDispersants in Oil Spill Response: Tropical Environments1This standard is issued under the fixed designation F 2205; the number immediately following the designation indicates the year oforigin

2、al adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon (e) indicates an editorial change since the last revision or reapproval.1. Scope1.1 This guide covers recommendations for use of chemicaldispersants

3、 to assist in the control of oil spills and is writtenwith the goal of minimizing the environmental impacts of oilspills. Aesthetic and socioeconomic factors are not considered;although, these and other factors are often important in spillresponse.1.2 Each on-scene commander has available several me

4、ansof control or cleanup of spilled oil. In this guide, use ofchemical dispersants should not be considered as a last resortafter other methods have failed. Chemical dispersants shouldbe given equal consideration with other spill countermeasures.1.3 This guide presents general guidelines only. The o

5、il isassumed to be dispersible and the dispersant to be effective,available, applied correctly, and in compliance with relevantgovernment regulations. Oil, as used in this guide, includescrude oils and fuel oils. Differences between individual dis-persants and to a certain degree, differences betwee

6、n differentoils are not considered.1.4 This guide is one of several related to dispersantconsiderations in different environments. The other standardsare listed in Section 2.1.5 This guide applies to marine and estuarine environmentsbut not to freshwater environments.1.6 In making dispersant use dec

7、isions, appropriate govern-ment authorities should be consulted as required by law.1.7 This standard does not purport to address all of thesafety concerns, if any, associated with its use. It is theresponsibility of the user of this standard to establish appro-priate safety and health practices and

8、determine the applica-bility of regulatory limitations prior to use.2. Referenced Documents2.1 ASTM Standards:2F 1209 Guide for Ecological Considerations for the Use ofOilspill Dispersants in Freshwater and Other Inland Envi-ronments, Ponds and SloughsF 1210 Guide for Ecological Considerations for t

9、he Use ofOilspill Dispersants in Freshwater and Other Inland Envi-ronments, Lakes and Large Water BodiesF 1231 Guide for Ecological Considerations for the Use ofOilspill Dispersants in Freshwater and Other Inland Envi-ronments, Rivers and CreeksF 1279 Guide for Ecological Considerations for the Use

10、ofOilspill Dispersants in Freshwater and Other Inland Envi-ronments, Permeable SurfacesF 1280 Guide for Ecological Considerations for the Use ofOilspill Dispersants in Freshwater and Other Inland Envi-ronments, Impermeable Surfaces3. Significance and Use3.1 This guide is meant to aid local and regio

11、nal spillresponse teams who may apply it during response planning andspill events.3.2 This guide presents data on the effects of surface oil,dissolved oil and dispersed oil on components of tropicalenvironments. These data can aid in decision-making related tothe use of dispersants to minimize envir

12、onmental damage fromoil spills.4. General Considerations for Making Dispersant-UseDecisions4.1 The decision of whether to use or not to use dispersantsin a given spill situation involves trade-offs. Dispersing a slickat one site temporarily introduces more oil into the watercolumn at that site than

13、would be there if a surface slick floatedover it. Therefore, adverse effects on water column organismsmay be increased at that site so that adverse effects can bedecreased at other sites.4.2 Dispersant use is primarily a spill control method, not acleanup method. Such use can give spill response per

14、sonnelsome control over where the impacts of a spill will occurwhatever types of impacts they may be. Since some environ-ments are known to be more vulnerable to the longer-lastingimpacts of spilled oil, an acceptable trade-off may be to protectthose environments by dispersing an oil slick in a less

15、 sensitive1This guide is under the jurisdiction of ASTM Committee F20 on HazardousSubstances and Oil Spill Response and is the direct responsibility of SubcommitteeF20.13 on Treatment.Current edition approved April 1, 2007. Published May 2007. Originallyapproved in 2002. Last previous edition approv

16、ed in 2002 as F 2205 02.2For referenced ASTM standards, visit the ASTM website, www.astm.org, orcontact ASTM Customer Service at serviceastm.org. For Annual Book of ASTMStandards volume information, refer to the standards Document Summary page onthe ASTM website.1Copyright ASTM International, 100 Ba

17、rr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.or less productive environment. In general, the net environ-mental benefit of dispersant use versus non-use should beevaluated. The net environmental benefit of a particular coun-termeasure involves evaluating benefits and

18、 disadvantages ofthe particular technology being evaluated, versus other cleanupmethods or no action, on the habitat or ecosystems involved inthe area. Environmental benefit analysis is best conductedbefore the spill.4.3 In this guide, environments that are most vulnerable tothe longer-term impacts

19、of oil contamination are identified.Protection of these environments is recommended as a highpriority, by means of dispersants or other methods.5. The Tropical Environment5.1 Tropical environments encompass many different habi-tats. This guide will cover those habitats that are important interms of

20、decisions to use dispersants. The applications ofdispersant to open waters and waters of depth greater thanabout 10 metres will not be covered here and is covered byother guides listed in Section 2. Shallow waters and habitatsassociated with mangroves, seagrasses and coral reefs areimportant conside

21、rations. Habitats other than those such assand beaches, mudflats, cobble beaches and rocky shores maybe common in certain localities but are generally less-sensitiveand are covered in the guide on temperate environments.5.2 Mangrove ecosystems are intertidal forests dominatedby various species of wo

22、ody halophytes that are commonlycalled mangroves. There are many families and species ofmangroves (1-4)3. Mangrove ecosystems occur in tropicallow-energy depositional areas. Mangroves tend to furtherpromote the deposition and recycling of organic and mineralmatter. Their extensive root systems are v

23、ery important instabilizing intertidal sediments (3). Adult mangroves form thestructural basis for the mangrove community in that theyprovide attachment sites for many species of animals andshelter for many others.5.2.1 Mangrove ecosystems contribute to the productivityof tropical marine ecosystems

24、where they play the same butmore important roles as do salt marshes in temperate climates.Mangroves are important as nursery areas as well as for thedetritus that they supply to the surrounding communities (3).Much of the worlds fish populations depend on detritus andremineralized nutrients exported

25、 from mangrove areas (5).5.2.2 Mangrove forests dominate much of the worldstropical shoreline; many are adjacent to tanker routes, oil fieldsand refineries. The low energy characteristic of mangroveforests leads to the entry and retention of oil in these environ-ments.5.3 Coral ReefsCoral reefs are

26、structures created andmaintained by the establishment and growth of hard corals andcoralline algae. They may be comprised of emergent orsubmergent reefal zones, or a combination of both. Geomor-phically, barrier and fringing reefs protect the insular andcontinental coastlines which they border from

27、erosion. Typi-cally, the coral reef provides habitat for a large variety ofattached plants and epifauna, infauna, mobile invertebrates,and fishes. The large number of economically importantspecies they support make reefs locally important in commer-cial and sport fisheries. The resultant high divers

28、ity andabundance of reef associates and the functional and spatialdominance of corals and coralline algae are the essentialcharacteristics of coral reefs.5.3.1 Coral reefs are circumglobal in the tropics and sub-tropics between the northern and southern hemispheric 18.5Cclimatic isotherms. A majorit

29、y of coral species and the mostdiverse reefs occur in Indo-West Pacific seas. Tropical WestAtlantic and Eastern Pacific reefs are generally less diverse interms of corals and reef associates.5.4 SeagrassesSeagrasses can be found in shallow marineenvironments from the tropics to Polar regions. This g

30、uidefocuses on those located in tropical waters. Seagrass beds forma discrete ecosystem that traps detritus derived from terrestrialand marine sources, and then exports large quantities of plantand animal materials, including leaf and root fragments,dissolved organic matter, and detritus, to the ope

31、n sea. Thepresence of an extensive network of roots and rhizomesfacilitates the sediment-binding ability of the grass beds; theseagrass leaves effectively retard currents, thus promotingsedimentations of organic and inorganic materials around theplants.5.4.1 Seagrass communities are among the most p

32、roductiveof natural ecosystems. Seagrass leaf blades support largenumbers of epiphytes which can equal the biomass of the grassitself. Major food chains are based upon a variety of epiphytesand associated organisms. Active sulfur, nitrogen, phosphorus,and carbon cycles are maintained through the sed

33、iment-plant-water interfaces, and the dense interlacing mat of vegetationprovides ideal cover for foraging marine fauna as well asshelter and protection for larval and juvenile forms.6. Effects of Oil and Dispersed Oil on Tropical Biota6.1 MangrovesMangroves are primarily impacted by oilby three dif

34、ferent routes; through the oiling of the pneumato-phores, or breathing pores typically located on special aerialroots or stems, through oil absorption from the water columnand through oil absorption through the roots from contami-nated soil/sediment and ground water (6-12). Mangroves withoil on pneu

35、matophores may die within about 5 to 7 days,depending on oxygenation conditions at the site (13-15).Mangroves may die from high concentrations of oil in thewater column (16-18). The third route of oil impact onmangroves, through oil absorption from the soil, is also welldocumented (19-22). Oil in ma

36、ngrove-dominated sedimentscan cause long-lasting effects and degrades only very slowly(23-27). Sublethal effects including leaf loss, deformations,and low growth can persist for five years after the spill event(8, 9, 28). Replanting mangroves, a primary restoration methodis successful in soils with

37、reduced hydrocarbon content (29-33). Natural regrowth occurs, but occurs slowly (34-36).Countermeasures which reduce the amount of oil arriving intothe mangrove area are suggested (37-39).6.1.1 Low levels of oil from either dissolved/dispersed oil inthe water column or in the sediments cause a varie

38、ty ofsub-lethal effects on mangroves, including leaf loss, reduced3The boldface numbers in parentheses refer to a list of references at the end ofthis guide.F 2205 02 (2007)2growth of adventitious roots, abnormal pneumatophores andmineral imbalance, and slow growth rates (40-43). Studiesshow that th

39、ese effects will persist from 1 year up to 7depending on amount of oil and environmental conditions.6.2 Biota Associated with Mangrove ForestsMangroveforests provide shelter and support for an extensive system ofbiota including algae, crustaceans, and molluscs. Dissolvedand dispersed oil can cause l

40、ethality to mangrove biota at levelsas low as 20 ppm and naphthalene as low as 0.4 ppm onprolonged contact (42-51). Studies have shown that the abun-dances of species inversely correlated with the apparent oildamage (52). Other studies have shown that the specificnumbers of a given species did not n

41、ecessarily correlate withoil content (53, 54).6.3 Coral ReefsCorals can be exposed to oil by twomodes, direct oiling and through the uptake of dissolved ordispersed oil. Direct oiling occurs rarely but can result inextensive mortality. The uptake of dissolved and dispersed oilcan result in severe mo

42、rtality at levels as low as 12 L/L forprolonged exposures (55). Corals are not usually subject toharmful concentrations of water-borne hydrocarbons by thepassage of a slick overhead and are typically unaffected(56-59). Similarly corals have been shown to reject particles ofoil larger (60 m) than dis

43、persed droplets (60). Corals are,however, particularly susceptible to high concentrations ofdissolved and dispersed oil and this may lead to long lastingeffects or mortality (42, 43, 47, 61-64 ). Because dispersantsmove oil into the water column, they may increase the effect ofthe oils on corals (5,

44、 65). Exposure of corals to about 20 to 50ppm of dissolved or dispersed oil showed that behavioralreflexes were induced in corals, however depuration was notedwithin a week and recovery within a few weeks (66-68). Somelong-lasting effects of low-level exposure was observed, in-cluding reduced growth

45、 and deformation.6.4 Biota Associated with Coral ReefsCoral reefs provideshelter and support for an extensive system of biota. Prolongedexposure to dissolved and dispersed oil can cause lethality toreef biota at levels as low as 20 ppm (12, 42-47, 50, 51, 69-71). Studies have shown that the abundanc

46、es of species inverselycorrelated with apparent oil damage (72). Increasing amountsof oil availability, such as through the use of dispersants,increases the exposure of organisms to oil (73, 74).6.5 SeagrassesSeagrasses can be exposed to oil by twomethods, direct oiling and through the uptake of dis

47、solved ordispersed oil. Direct oiling occurs rarely but can result inextensive mortality (17). The uptake of dissolved and dispersedoil can result in severe mortality at levels as low as 100 g/L(75). Seagrasses are not usually subject to harmful concentra-tions of water-borne hydrocarbons by the pas

48、sage of a slickoverhead and are typically unaffected (76-78). Seagrasses are,however, particularly susceptible to high concentrations ofdissolved and dispersed oil and this may lead to long lastingeffects or mortality. The lethal toxicity to seagrasses varies verymuch with species, and is between 75

49、 to 125 ppm in 100 h (79,80). Use of dispersants may increase the exposure of sea-grasses to oil (81, 82).6.6 Biota Associated with SeagrassesSeagrasses provideshelter and nutrients for an extensive system of biota (83, 84).Dissolved and dispersed oil can cause lethality to these biota atlevels as low as 20 ppm (12, 42-47, 50, 51, 69-71 ). Increasingamounts of oil availability, such as through the use of dispers-ants, increase the exposure to organisms (73).7. Recommendations7.1 Dispersant use decisions must be based on the netenvironmental benefit analysis of use versu