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3.7 Seaweed and Sediments (Topinka, Bigelow Laboratory for Ocean Sciences) In support of an investigation on the impact of the spill on macroalgal population recovery and growth, a series of plant and adjacent sediment samples was analyzed by GC to determine if and to what extent AMOCO oil was associated with the plants (Table 27). The data presented in Table 28 in conjunction with a consideration of Figures 3.81 and 3.82 illustrate that while several of the plant samples do contain weathered oil (see Fig. 3.81) the n-alkane, pentadecane (n-C^) , is the most abundant biogenic component in all samples. The distribution of biogenic components in general (Fig. 3.82) can be seen as contributing markedly to the total hydrocarbon levels even in the "oil-impacted" tissues. GC/MS results of an "oil impacted" plant's aromatic hydrocarbon fraction (Table 29) indicate that again the P and DBT family series are the most abundant aromatic compounds present. In this sample the P compounds are, in total, more abundant than the DBT series, but the C3DBT are still the most abundant group (8400 ppb) . TABLE 27. AMOCO CADIZ chemistry program; seaweed samples (Topinka). Frequency June 1979 15 Plant + 7 Sediment August 1979 2 Plant May 1980 3 Plant Summer 1980 12 Plant TOTAL 32 Locations Var ious GC/MS One Seaweed Sample 94
TABLE 28. Summary of analytical results; seaweeds, summer 1980. Gravimetr ic Sample t x (pg/g) f 2 (ug/g) HC-4-1
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Na/JA/CNfiXO 0
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ECOLOGICAL STUDY OF THE AMOCO CADIZ
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Preface TABLE OF CONTENTS I. Physic
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PREFACE At approximately 11:30 p.m.
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In November 1979, an international
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CNEXO-NOAA Joint Scientific Commiss
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MICROBIAL HYDROCARBON DEGRADATION W
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Chemical Hydrocarbon Analyses Perfo
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147, 156, 170, 178, 184, 192, 198,
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The microbial hydrocarbon biodegrad
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TABLE 7. Biodegradation of 9-methyl
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The detailed gas-chromatographic an
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TABLE 13. Hydrocarbon concentration
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TABLE 17. Hydrocarbon concentration
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TTTl n rrffl KMIIMCi WOU^I ! I .Dm.
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o z o 5- 3- UJ >4 UJ - cc 2- I ll F
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z o 4. 3_ 2- t- 1 _ < K o z o 1_ o
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CONCLUSIONS Microbial degradation a
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LIQUID 5AK?lE CCNTftit-'JGAriOH + F
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The saturated hydrocarbons were mos
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acteria of the genus Moraxella, ind
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2. CONTINUOUS CULTURES In continuou
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INTRODUCTION All fate and effects s
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2.1 Sediments and Sediment Cores (E
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TABLE 2. Focus of GC/MS analyses. S
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T.ssue Semoie S50 grams Wet) HI Dis
Page 58 and 59: ae = E3£\CE '.tC'-SSE S* -•* 3 S
Page 60 and 61: TABLE 3A. Weathering of AMOCO CADIZ
Page 62 and 63: fli-Liftim Mi.u".- i I 7 1 1 5 6 /
Page 64 and 65: 3.2 Surface Sediments (Atlas, Unive
Page 66 and 67: _l I I I I I L_ a •BIOGENIC P •
Page 68 and 69: TABLE 6. Replication of hydrocarbon
Page 70 and 71: -I—i i i i i i i i—i—i—I t
Page 72 and 73: t i I hn I 94 n,, , i i I ABCOEFGHI
Page 74 and 75: C30BT:177ng g 1 * ? » I—I—I I
Page 76 and 77: marker compounds, the C3 dibenzothi
Page 78 and 79: TABLE 8. AMOCO CADIZ sediment sampl
Page 80 and 81: TABLE 11. St. Michel en Greve/Lanni
Page 82 and 83: TABLE 14. L'Aber Benoit GC/MS resul
Page 84 and 85: 3.4 Sediment Cores (Ward, Montana S
Page 86 and 87: ' TABLE 16. L'Aber Wrac h sediment
Page 88 and 89: !•[ 220 = f occEMeea 1979 AUGUST
Page 90 and 91: 10 120 1000 no g 400 600 ALU ISO AL
Page 92 and 93: The AMC-4 cores appear dominated by
Page 94 and 95: 3.5 Oysters and Plaice (Neff, Batte
Page 96 and 97: The GC traces for the impacted oyst
Page 98 and 99: m/e m/8 m/e Lja.i t: J b l| c I "II
Page 100 and 101: -* I I I I ABCDEFGH IJ K LMNOPQRSTU
Page 102 and 103: AROMA IK S SATURATES 4-1 FIGURE 3.7
Page 104 and 105: TABLE 20. AMOCO CADIZ chemistry pro
Page 106 and 107: TABLE 24. Results of ISTPM fish ana
Page 110 and 111: ma. w p FIGURE 3.81. HC-4-1 seaweed
Page 112 and 113: 9) Oysters were initially heavily i
Page 115 and 116: STUDIES OF HYDROCARBON CONCENTRATIO
Page 117 and 118: sample 1 - extraction (toluene meth
Page 119 and 120: TABLE 1. Hydrocarbon content of lie
Page 121 and 122: TABLE 3. Chromatographic analysis o
Page 123: 1A _jiU' IB •JlIw '3 L Pr i 2A 2B
Page 126 and 127: CD o 0. - f 2104 "*. vli . ! i » -
Page 128 and 129: A IB A HC. SATURES S M C C [HiLJJL
Page 130 and 131: The relative contents of saturated
Page 133: 31-03-78 22-11-78 20-06-79 17-1-80
Page 136 and 137: PORTSALL 23-3-78 FPD AW 22-11- 78 F
Page 138 and 139: 31-03-78 22-11-78 20 - 06 - 79 17-
Page 140 and 141: STATION 6 i—r 3400 3000 1600 31-0
Page 142 and 143: PORTSALL 23-3-78 FPD AW 22-11-78 FP
Page 144 and 145: Photometry Detection (FPD) as well.
Page 146 and 147: 1 r PIODUI7S F.ECUPEF.ES BRUT DECAN
Page 148 and 149: The chromatogram of the saturated h
Page 150 and 151: etween the end of March and early A
Page 152 and 153: certain chemical species which are
Page 154 and 155: It should be noted that a sample ta
Page 156 and 157: REFERENCES CITED Aminot, A., 1981,
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affected a very large section of th
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OIL POLLUTION IN THE WESTERN ENGLIS
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atio of more than 100 is an index o
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TABLE 4. Comparison between hydroca
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FIGURE 7. Sampling stations in the
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IBB 000,- HC CPPM] ib me. lass. 100
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ACKNOWLEDGMENTS We would particular
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METHANE-PRODUCING BACTERIA POLYMERI
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AMOCO CAQiZ ® BE" 'LOUT U A8ER .^"
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and methanolic (f~) fractions for o
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14 99%) from New England Nuclear; n
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concentrations were extremely low (
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(A) Oiled Estuary Mudtiat cms " i l
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TABLE 3. Aromatic Hydrocarbons in B
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TABLE 4. 11 *C0 2 + 1
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IGO 3-6 cm slurry IGO 3-6cm slurry
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FRESH OIL hk UjlAdU-uJM^vA. i^w*XaA
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TABLE 7. Effect of AMOCO CADIZ Mous
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14 TABLE 10. Effect of Hydrocarbons
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pounds were, however, noted at dept
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effects of additional heavy oiling.
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Centre Nationale pour ' 1 Exploitat
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S^rensen, J., D. Christensen, and B
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REPONSES DES PEUPLEMENTS SUBTIDAUX
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Les nouvelles populations caracteri
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TABLEAU I. L' evolution des peuplem
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B Dui © ® Du 2 © Sf FIGURE 4. Ev
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populations initiales durant la pre
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vs w DU w VS/ FV W DU,B SHV W ' \ /
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Connell, J.H. et R.O. Slatyer, 1977
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Les unites cenotigues correspondant
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les peuplements de la baie de Morla
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R, E c a ~ a H CO 3 -> E ;j cu R. a
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-
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leurs du meme ordre qu'avant la pol
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N/m 10 10 10 10 • -* Cycle normal
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3.2.3.2) Peuplement des sables tres
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Richesse specifique (fig. 10) D'avr
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N.m-2 300^ 250 200- 150 100 50 -•
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propor tionnels aux quantities d'hy
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Den HARTOG, C. 8 R.E.W.H. JACOBS, 1
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ETUDE EXPERIMENTALE D'UNE POLLUTION
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I. Pump2 Pumpl HL_Q I § i I ,1 1 I
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3000 1500 1000 - FIGURE 2. Evolutio
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L'evolution des Copepodes harpactic
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La sensibilite de cet indice semble
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La biomasse est sensiblement plus f
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BIBLIOGRAPHIE Andrassy, I., 1956, D
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Pearson & Rosenberg, 1978, Macroben
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INTRODUCTION Dans le cadre du suivi
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Pigments chlorophylliens RESULTATS
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apparente en decembre 1978 et aout
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Pheo (vg/q ) Ca (pg/g) 5 5 to 15 \
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Les conditions meteorologiques (fac
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TABLEAU 2. Evolution temporelle des
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On peut aussi expliquer , du moins
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A Brouennou, quatre groupes ecologi
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un groupe de sabulicoles epi- et en
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schema des mecanismes regulateurs d
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Gargas , E., 1970, Measurement of p
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LONG-TERM IMPACT OF THE AMOCO CADIZ
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The first type is due to the direct
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RESULTS Tissues from 134 specimens
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Table I. Distribution of patholocie
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a. B o r— IT) —
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antenai, and longitudinal spiral ro
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epresented an inflammatory response
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lateral nuclei were present. The ci
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There was also some indication, bas
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This method, based on the glucose o
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Table 4 . Concentrations of total a
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Table 6 . Concentration of aliphati
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sediments which is dominated by hig
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Table 9 . Concentration of aromatic
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COn,pOUnd Table 11 . Concentration
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Table 12. Concentrations of total a
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. Table 14. Concentration of alipha
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Date/Sample April 1979 (13) Whole F
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Table 17 . Concentration of total l
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laboratory (Wardle, 1972). In the l
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Table 23. Concentration of ascorbic
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Table 25 • Concentration of free
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ange. Dominant tissue-free amino ac
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Table 28 Concentration of free amin
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Table 30. Concentration of free ami
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Table 32 . Concentration of free am
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oil-polluted Abers and from nearby
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REFERENCES CITED Anderson, J.W. , 1
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McCain, B.B., H.O. Hodgins, W.D. Gr
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RETABLISSEMENT NATUREL D'UNE VEGETA
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INTRODUCTION Le retablissement d'un
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Nous distinguerons alors les phases
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Situation 3) Territoires fortement
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Plus precisiment le codage correspo
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Figure 3. Marais 6-Etat en 1979 (le
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Figure 5. Marais 6-Etat en 1981 (le
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Commentaires Mis a. part un petit n
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- Marais 3. Ce transect, situe en m
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TRANSECT 'VVATS 5 Figure 8. Transec
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05 (11 O ; cd 00 i I i I i I I I I
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'igure 9 Transect permanent-Marais
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Commentaires - Estuaire de Kerlavos
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1 - appel a la notion de compositio
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Figure 12. T'orphologie comparee d'
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- les plantes survivantes -initiale
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General RESTORATION OF MARSH VEGETA
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FIGURE 1. Marsh west of the bridge
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1979 Plantings Based on our prelimi
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FIGURE 6. Digging Puccinellia along
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FIGURE 10. A 6.5-cm diameter soil a
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In September, we made 9 additional
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FIGURE 16. Creek bank without veget
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FIGURE 19. Eroding creek bank at He
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'^^Wr ./".#" -•: rst^ s8H.*r FIGU
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FIGURE 26. Experimental planting es
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Elevation All elevations are given
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FIGURE 27. Map of study area on nor
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Keri&vos FIGURE 30. Map of study ar
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^~~ -
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TABLE 4. Survival of two types of t
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area (12 m 2 ) , and was an excepti
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TABLE 8. Aboveground dry weight of
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,^-^ FIGURE 37. Several 2-year old
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FIGURE 38. Experimental planting at
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fr J1MI FIGURE 40. Experimental pla
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Puccinellia were planted at one of
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FIGURE 44. Preliminary planting of
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Transplant Time Requirement It is d
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is about 540 cm^ or over 20 times t
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FIGURE 53. Plant shown in Figure 51
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FIGURE 56. Experimental planting of
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ACKNOWLEDGEMENTS Cooperation with o
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LITERATURE CITED Baker, J. M. , 197
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ETUDES MICROBIOLOGIQUES ET MICROPHY
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HMMME NTHWL SWIRLING SITES Referenc
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dans les chenaux (carottes de 30 a
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degres d'une part, et entre les sta
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Schorres peu polities, CI et Bl CI
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L'activite enzymatique dans cette s
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chenaux : Conclusions sur le biotop
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Les schorres Les schorres, par cont
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stations TABLEAU 2 IIYDROfARUUKES D
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Ci 1 12-14 )uiH 79 2-7 oct 79 23-25
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E •" * — lissMs .-*. K V- v..
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FIGURE 8 Evolution temporelle des c
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150- 100 50- 150- 100- 50 446 *o
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REFERENCES BIBLIOGRAPHIQUES Atlas,
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1964-1982, COMPARAISON QUANTITATIVE
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453
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EFFETS DE LA MAREE NOIRE SUR LES PE
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ESPECES En 1980, on a pu cartograph
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3- EVOLUTION GLOBALE II semble s'am
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COUREE DE L EVOLUTION DES BIOMASSES
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464
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CO 00 466
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468
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470
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472
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I s
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476
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Q) 1
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