When was tone loc poplar

Zinn, eds. Putnam, M. Cambridge, Mass. Reed, J. Romeo, A. Rosati, G. Schiesaro, A. Fantuzzi and T. Papanghelis, eds. Smith, P. Stephens, W. Tarrant, R. Theodorakopoulos, E.

Martindale, ed. The Cambridge Companion to Virgil : Williams, G. Wiseman, T. Woodman, A. Du Quesnay and A. Woodman, eds.

Catullus : Poems, Books, Readers : See also Galand-Hallyn and Romeo For a symbolic analysis of shade within the Metamorphoses, see Jouteur , esp. She does not discuss the grove of Orpheus within this context, but sees the concept of shade in its use across the Metamorphoses as a dangerous presence, a conceptualisation that suffers slightly from its reductionist view of the ways in which Ovid draws upon a host of meanings and associations.

We have a parallel to the visit to Hades; again Orpheus wins back his wife, although for a short time, by his art. Before the sea and lands and everything the sky covered there was one face of nature to the entire world, which was known as Chaos. The heroic Orpheus was also known for singing a cosmogony Ap. Maltby s. One might further note that a different region in Epirus, Thesprotia, was said to contain an entrance to the Underworld, largely through affiliations with the Acheron; cf.

Hardie further notes Narcissus as akin to Tantalus in experiencing eternally deferred pleasure, never being able to attain the object of his desire; this makes his reading of umbra for unda interesting in light of the argument Lacki makes for the emendation of unda to umbra in the allusion to Tantalus at Heroides For the connection between the two passages, and the wider resonances between the Cycnus passage and the lament of Orpheus, see Fernandelli In in the grove of Orpheus, the sisters of Phaethon are not specifically designated as poplars, but are simply designated by the phrase nemus Heliadum.

Such a generalised designation is consistent with the picture of their metamorphosis in Book 2 , where the trees they become are not explicitly named. Elsewhere they become alders, as at Eclogue 6. Clausen ad loc. Poplars are also associated with the Underworld through the figure of Hercules, who fashioned a wreath of white poplar to mark his ascent from the Underworld; For the associations between Hercules and the white poplar, see Paus.

Servius ad Ecl. Nisbet and Hubbard , and esp. Knox ad loc. For Catullus 65, elegy, and the Virgilian Orpheus see Barchiesi Hinds and n.

Hymn 5. Knox ad ES 30 also identifies a link between this passage and the Horatian text. For Orpheus within the lyric tradition, see the sources collected in Reed Related to this idea of the locus amoenus , a few scholars have advanced the notion that the grove of Orpheus is connected to or reminiscent in some way of the Grynean Grove.

For these views, see Fabre-Serris and Jouteur For evidence of the Grynean Grove see van Groningen , ad Euphorion fr. Both groves are inclusive of an Ovidian-style tree catalogue, and incorporate notions of both sweetness and delight, and suggestive hints of the Underworld.

Garrison n. The Ovidian inamoena seems to be in dialogue with the Virgilian inamabilis of both Georg. Because it is tied to unda in both places within the Virgilian corpus, it would seem inappropriate for the strength of inamabilis to further cast over the grove that Orpheus creates, given its lack of running water; for analysis of the Virgilian use of inamabilis, and its affiliation with water, see Pelliccia ; cf. Ovid is careful to differentiate his account of the Underworld, a difference that is acknowledged when Orpheus is reunited with Eurydice: Orpheus sees the places he saw before et quae loca uiderat ante , Contr8ct C « Grant G No.

Environmental Protection M Street, S. Type of Report. SuppIem8nWy No- The Poplar Oil Company continued to accept. In EPA found PCBs in onsite ground water and soil which resulted in several emergency actions that included draining and regrading 2 retention ponds, diverting surface runoff to other retention ponds, removing offsite and incinerating , gallons of waste oil, treating and discharging offsite , gallons of contaminated surface water, and solidifying , gallons of sludge.

Two additional orders were issued ordering workplan development and incineration of materials in the pits, tanks, and heavily contaminated soil. See Attached Sheet Document Analy". Security a Report None Abstract Continued o The selected remedial action for this site includes draining onsite freshwater and retention ponds with offsite discharge and refilling; thermally treating contaminated soil, ash, and debris from the boiler house area with onsite disposal of ash if the ash can be delisted, otherwise offsite disposal in a RCRA landfill; demolishing and thermally treating or decontaminating.

Tq:af Site Name ani I. Wax identifies the items that cx:rrprise the administrative record- upon which the selection of the remedial action. EPA's remedy selection. EPA's Feasibility Study. A brief discussion on this issue is presented later in this document. Dtia1 of the selected Remedy '! C:I1dn Pq lar oil site are OJntaminated soils an:i sediments will be contained by a DI. A groon:iwater diversion trench will be installed ara:arx:i the site to prevent graJrXiwater fran pass:in3' through ccntaminated soils.

An att. Additionally, because the dioxin waste an:i contaminated material will, remain on-site, the selected remedy will provide for-lorg-te1:m monitor:in3'- - for groon:iwater, surface water, an:i performance of the t:rench:- ani cap. Site use am acoess restric, ions will be placed on the pJ:'q erty to ensuret". Discharge surface watar fran pords to CerneteIy Creek, with treatment if required. Backfill freshwater.

If material can not be decontaminated or thermally treated, contain material in an on-site cx:n::rete vault am place beneath the cap for tenporalY storage until proper effective disposal can be secured for the material. De-water site by natural groon:iwater flow to CeJretety creek.

Conjuct grcmrlwater an::l surface ,' Treatment is not a major Culp. SUmrrary of Risk C'1aracterization. Analytical Methods. Alternative 2. Al ternati ve 3A. Alternative Alternative 4A. Al ternati ve SA. Al ternati ve Alternative 6. LcnJ-Term Effectiveness an:i Pertnanenoe.

Reduction of 'I'oxicity, Mobilit;y, or Volume. Short-Term Effectiveness. State Acceptance. IJcatia1 of Diversim Tren:h, M. Irdwater It is southwest of the i11tersectioo of Chio Ralte ard Poplar street, ard imnediately south of CeneteIy creek' Figure East of Poplar Street, in the fai. Ird, especially irI relation to operation of the racetrack ard horse stables. Water for all hane. U'rler- 'Cjround ard. Three small treatment porrl!

The shale is. At the laskin Poplar oil site, gI"'OOlrlw'ater in the surficial aquifer flows in the weathered shale, till, ard.

Groun:lwater flow in the urrwe. D'dwater flows 0Jt of the ponds at a steep gradient in the earthen dikes on the c:lown;radient side of the pords. Much of the site surface consists of fill material. Surface elevatiens at or near the site ran:Je fran to feet above mean sea level msl , with elevations near the freshwater pord ard tanks rangirg fran to feet msl.

In , the U. In early , the united states Environmental Protection kJercy U. EPA corx1ucted an investigation at the site and detected polyc:hlorinated biJi1e. In and , the U. EPA perfonned several eme. EPA is 'the -lead -. Remedial Investigation RI. Activities included saI! DJrirg the winter of , the potentially responsible parties PRPs rem:JVed aR'roximately , gallons of waste oil anJ waste water, in response to an administrative order issued in August A third administrative order issued in FebruaIy ordered.

Work inclooed geq:t1ysical studies: bathymetric surveys: installation of nom torirq wells, and; sampl irq of grourrlwater, surface water, soils, an:! Jblic meeti.

EPA sent a special notice letter to a rn. EPA's preferred remedial alternative for the raskin Poplar oil site. Technical discussions bet'ween the U. EPA an:! EPA held an organizational meeti. EPA in atterrla. At that meeti. A section were discusser-1 an:! EPA provided the public with an opportunity to cxmrent on the u. Iniividuals were also enc::o.. All fonnal reports developed by the U. EPA are available at these locations. Notification of the availability of the doo.

In addition to the fonral reports, the U. EPA distrib. EPA held a fornal public meetirq at the Ashtal::W. EPA made presentations to the ccmnunity on topics such as: saIT1? EPA's preferred alternative. Followirq the presentations, the u.

EPA answered questions fran interested parties present at the Deetirg. A transcript of this meetirq is included as part of the h:bninistrative Record see h:bninistrative Record irrlex, attad1ed as Appen:lix A for the Iaskin Poplar oil site. As a result, the u. EPA organized the work into two operable units oos. Halogenated alkanes, ketones, ard polynuclear aranatic hydroc:. Organic contaminants were detected at la..

JJ'dw'ater at la.. Analytical results i1rli. JJ'dw'ater cont. On-site soil sanples for polYchlorinated d. Under U. Results did not indicate that.

It is a. Jblic health arrl. EPA g. Instead, all J tential concern for the Iaskin Poplar oil site are listed in Table Not every chemical reviewed had a critical toxicity value or an environmental criterion. HC7Wever, the chemicals that did not have such values or criteria occurred infrequently with no unifonn distr:ib.

Ition on-site or off-site. Review of the data indicated that anission of those chemicals fran the quantitative risk evaluation 'NOUld not substantially alter the conclusions of the risk asses.. Urder this asstmption, the as.. Grourrl water in this area contains PAHs, halogenated alkanes, and ketones. Certain levels detected exceed the U. EPA's Maxim. Non-carcinogenic hazard irdices ranged fran less than 1 to. Although these risks are significant, exposure is unlikely to. Grourrl water on-site is o.

The canbination of diversion trench. Carcinogens were not detected in water fran either pord. Organic and inorganic oontamiJ1a. Potential grourrlwater di. Because sane of the estimated values were below the U. EPA has net developed st. Infornation on soil irgestion exposures was reviewed and representative soil in;estion rates were selected.

Dennal absotption is also a potential exposure roote associated with soil contact. Because of this, risks associated with soil ingestion were ssumed to be representative of direct contact soil exposures.

The risk assessment identifie. Carcino;enic risk reaches a high of 2xlO-3 to a resident in the ooiler hci1se who in;Jests soil fran 0 to 14 feet with the highest detected concentrations of PAHs arrl PCBs. Soil arrl sediment. The presence of - contaminants in surface soil, sub-surface soil, arrl gro. Inhalation risks. Contact with contami.

Uncertainty factors in this particular site's risk assesSJT! Noncarcinogenic risks were estimated by calculatirq a Hazard Irrlex HI , the ratio of the exposure dose :to the acceptable Chronic intake. Cancer risks were estinated bymultiplyirq the average lifetime exposure dose by the CPF. In general, the RfD is an estinate with uncertainty spann. CPFs are presented in units of the inverse of milligrams of chemical per kilc:qram of body weight per day. EPA to estimate the CPF fran animal studies or human data assumes a dose-response relationship with no threshold.

Excess lifetime c:anc:ar risk is the i. In:i pI"C b3bility Le. Grc::urlwater '! SUrface Water '! A representative concentration for each d1emical detected was determ. Soil Prd:able average case doses for exposure were calculated based on ingesting 0. Worst case doses were calculated based on ingesting 1. Possible release mechanisms include volatilization of organic. EPA identified potential risks that shculd be addressed by remedial " response actions at the raskin Poplar oil site.

These risks are as. The FS identified tec:hnologies that cculd eliminate or reduce the risks for each of these media. A - cs-. The eight other al ternati ves r-a. The FS looked at alternatives involvirq treatJrent in order to reduce the toxicity, ItObility, or volurre of site wastes. Each of the eight remedial alternatives evaluated in detail is described briefly belo«. Section 9. EPA is required to evaluate a "No Action" alternative. No additional crsts or t:i1re would be required beyord the source rerroval action.

Firstly, retention ard freshwater pads wcW. The fresh water perd W'OUld be back filled with clean soil material. The boiler hoose W'OUld be demolished.

Materials amenable to decontamination would be decontaminated, an:i disposed of in an off-site sanitary larrlfill. Dioxin-oontaminated soils, ash, arrl debris fran within the boiler hoose W'OUld also be disposed of in the ooncrete vault on-site. The greenhouse area would then be regraded an:i vegetate::i to alla. A 2 foot clean soil caver would be placed over all soils that excee::i lxlO-6 excess lifetime cancer risk levels ard total hazard Wex of one.

The soil. Additionally, the program wcW. If the levels L: contaminants in grourrl water do not increase over time, the sanplirq schedule wcW. A statistical test wcW. Irpose:i to prahihit site? Introducing the best selling drumset of all time Export Series returns. Designed for minimal shell interaction, they have a small footprint and low-mass for maximum resonance and sustain.

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