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AppendiI C3. (cont.) Coo c.eo lratiolU, nfl/IE Isotonic comlMlsitioD(sUr. "-\ Offsbore [osbore Offs bore Iashore TPAH .. A. 11 A •• Py BA Chv Bh' BkF B.P B.P P" I . DBA BP 364 0.15 9.25 71.6 22.0 45.2 33. 1 42.2 24 .6 15.6 2.75 19.6 9.63 14.0 11.4 6.5 35.6 887 0.75 23.8 97.8 29.0 158 146 79.2 11 0 24.5 28.0 31.5 59.2 49.2 l3. 5 0.0 30.5 NlA - -28.4 - -26 .5 -26.1 - N/A - -26.9 - -26.0 -25.2 - -24 .9 - 26'
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POLYCYCLIC AROMATIC HYDROCARBONS IN
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composition. Portions ofthe lake th
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TABLE OF CONTENTS . ABSTRAcr._._ _
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6. CONCLUSIONS_._ _....._._._ _ ._
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FIGURE 3.104 CONfIGURATION OF ISOCH
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FIGURE 4 .2.12 SAMPLES AND PROMINEN
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fIGURE 5.3.1 DESCR1Pl1VE MODEL OF S
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APPENDIX B 3 _ T HEoerwt Of A PtUNC
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Ip » Ideno(l,2.3 cd)pyrene NIST =
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Figure L 1.1 The 16 parental polycy
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After release by the primary source
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decomposition processes (O'Malley e
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Figure 2.1.1 The Great Lakes draina
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;: Duluth Chicago 1 J Lake Superior
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are the Black River, the Cuyaho ga
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Figure 1.1.5 The pattern of permane
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sedimentary basins, Western. Centra
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Figure 2. 1.8 Summer (July) air and
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Natural Resources: The lower Great
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American waters under the current U
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continuously overflowed com bined s
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3.1 EXPERIMENTAL 3. METHODS 3.1.1 S
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Table 3,1.1 Locations and types ofs
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Figure 3.12 Extraction and purifica
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hexane. 2) the unsaturated aliphati
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this problem. Ratios ofthe two stab
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Figure 3. 1.4 Configuration ofIsoch
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3.2.1 UNl- AND BIVAJUATE METHODS Th
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f igure 3.2. 1 Mean and range (± s
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utilized the same instrument (Isoch
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Selecting lIt1J'iahlu: It was demon
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w- _ 71
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seven variables with fewer missing
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analysis also employed a greate r n
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description. The second cluster ana
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elationships between different site
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Figure 4.1.3 Regression ofthree fir
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Figure 4.[.5 Isotopic composition (
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Figure 4.1.6 Weights ofvariables (c
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Figure 4.1.8 Distri bution ofsample
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those at the majority ofstations. S
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Ion, 969, 971, 357, 358). In additi
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Figure 4.2.3 Samples and prominent
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analysis supported some ofthc previ
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, ", Is , , >\ ryr " II ,- - , I ,
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11'
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sources (Fi g. 4.2 .5c). This compo
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Figure 4.2.7 The relative contribut
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".1.1.2 Miring CllrIIU (isotopic co
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Figure 42.9 Samples and promin ent
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Figure 4.2. 13 Samples and prominen
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It is difficult to differentiate be
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Figure 4.2.18 Weights ofvariables (
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Figure 42.19 Distribution ofsamples
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5.1 SPATIAL DI STRIBUTION s. DISCUS
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f igure 5.1.1 Zones coinciding with
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f igure 5. 1.2 Average and range (
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Figure 5.1.4 Zones (clusters) in th
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Figure 5.1.5 Direction ofthe mean s
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The location ofthe third station at
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Figure 5.1.7 Station locations and
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5.1.4 and Section 4.1.2). This clus
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Figure 5.1.1 1 Statioo locations an
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unaffected by the contaminated flow
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this station is die clo$esf to the
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samples and sources (Fig. 52.1 and
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There is yet another observation po
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with the relative contribution ofdi
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Table S.l.1 Six dusters identified
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the three previous ly identified zo
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contribution from petroleum related
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(Fig. 4.2.7). Finally. this site co
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Snow melt and sewer releases seem t
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importance ofcombustion-derived PAR
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Intens ity o(degradation (the South
Page 239 and 240: where this importance is somewhat r
Page 241: Figure 5.2.5 Station tocatices andz
Page 244 and 245: :2 for molecular composition assume
Page 247 and 248: ange of Slatistica1 variat ion of t
Page 249: Figure 5.].1 Descriptive model ofso
Page 252 and 253: conveyed into the river through dir
Page 254 and 255: molecular composition. Its applicat
Page 256 and 257: Canton L. and Grimal t 1. O. (1992)
Page 258 and 259: Howell E. T., Marvin C. H., Bilyea
Page 260 and 261: Olson F. C. W. (l950) The currents
Page 263 and 264: Willett P. (1981) Similarity and cl
Page 266: t Apprndb AI. [cout.) bl S,.lioD A<
Page 271 and 272: Appendill A6. The two-component mas
Page 273: Appendix A7. (cont.) Xl. = X llVt r
Page 277: • ass
Page 281: Appendix 82. (cont.)
Page 285: Appendix IU. (cant.) oj Tue Dec 24
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