OHited States
             Environmental Protection
             Agency
SEPA       Research and
             Development
             ABSTRACTS  and INDEX  TO PUBLICATIONS
             RELATED  TO MICROBIAL  ECOLOGY,
             BIOCHEMISTRY,  GENETICS and
             BIOTECHNOLOGY
             Prepared by
             Environmental Research
             Laboratory
             Gulf Breeze FL 32561
             MICROBIAL ECOLOGY AND BIOTECHNOLOGY BRANCH

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                             About This Publication











    Thi Mierobial Ecology and Biotechnology Branch* Environmental  Research




Laboratory, Gulf Breeze, FL is responsible for conducting a research  program




to!  1) descriDe and model microbiological interactions tuith pollutants*




including their biodegraciation rats* sorption, -transport* and resultant




affects on organisms; and 2) develop methods and principles u/hich  assess




tha potential acologtcal risk associstad usith the application of




genetically engineered organisms (biotechnology) to the environment,




including survival* growth, genetic stability* and ecological hazard.




    This publication lists all in-house and extramural reports issued




by the Microbial Ecology and Biotechnology Branch since 1973* including




in-press and in-prsparation manuscripts.




    An asterisk oaside the Gulf Breeze Laboratory contribution number* e.g.




:RL,GB# or ERL»G3X** indicates that the item is no longer available from




the laboratory.  If it is available from NTIS, Sprxngfield* Vfl* tha order




nunber is given after the citation.  Written requests for copies of items




Listed in this publication should be addressed to the Laboratory Librarian.




For phone requasts, plaase call C904) 932-5311 or CFTS) 686-9011,  ext 218.




Plaase cita tha ERL»G8 contribution number when requesting reprints.
                                                        Henry F. Enos



                                                        Laboratory Director
Preparation Date:




Septanoer 1935



                                       ii

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TABLE OF CONTENTS                                             PftGE







ABOUT THIS  PUBLICATION.	   ii




TITLES  *NO  ABSTRACTS	     1




KEYWORD TITLE  IND5X.....	    48




AUTHOR  INDEX.......	    61

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ASDtLAL, AHMED T.H.,  EMILY  H.  KENNEDY.  AND DONALD G. AHEARN.  1977.
PURIFICATION AND CHARACTERIZATION  OF 4  NEUTRAL PROTEASE FROM SACCHARQMYCQPSIS
LIPOLYTICA.  J, BACTERIOL.   130(3):1125-1129.  CERL,G8 XQ03*)-

   SACCHAROMYCCPSIS  LTPOLVTICA 37-1  PRODUCED TWO INDUCI3LE  EXTRACELLULAR
   PROTEASES.  ONE   UMDER  NEUTRAL  03 ALKALINE GROWTH CONDITIONS  AND  THE
   SECOND  UNOER ACID CONDITIONS.  SECRETION OF THE NEUTRAL  PROTEASE  WAS
   REPRESSED  IM  THE  PRESENCE OF  GLYCERQL OR  GLUCOSE,  BOTH  OF  WHICH
   SUPPORTED  RAPID  GROWTH  OF  THE  ORGANISM. AMMONIUM IONS ALSO  REPRESSED
   THE SECRETION OF  THE ENZYME. THE  NEUTRAL PROTEASE ACTIVITY  CQPURIFIED
   WITH ESTERASE ACTIVITY  DURING AMMONIUM SULFATE FRACTIONATION»
   CHROMATOGRAPrtY  ON DIETHYLAMINOETHYL-CELLULOSE. AND GEL FILTRATION  ON
   SEPHADEX G-150. THE MOLECULAR WEIGHT OF THE ENZYME WAS ESTIMATED TO 3E
   42,000  3Y  SUCROSE  DENSITY GRADIENT  CENTRIFUGATIQN  AND  38,500  8Y
   PQLYACRYLAMIOE  GEL ELECTROPHQ^ESIS  IN THE PRESENCE OF SODIUM  DODECYL
   SULFATE. THE PURIFIED  ENZYME HAD  A PH OPTIMUM OF 6,8
   PHENYLMETHYLSULFONYLFL'JORIDE  INHIBITED  BOTH  PROTEASE  AND  ESTERASE
   ACTIVITIES, INDICATING  THE  PRESENCE  OF A SERINE RESIDUE IN THE  ACTIVE
   CENTER. PROTEASE, 3UT  NOT ESTERASE,  ACTIVITY WAS SENSITIVE TO
   ET.HYLENECIAMINETETRAACcTATE ^ND  WAS  SIGNIFICANTLY ACTIVATED 3Y
   DIVALENT   IONS.   DITHIOTHREITOL  INHIBITED BOTH PROTEASE  AND  ESTERASE
   ACTIVITIES,  INDICATING  THE PRESENCE 0^ A CRITICAL  DISULFIDE  BRIDGE.
   THE  ENZYME HYDSOLYZE3  CASEIN (KM  = 25.6 MM) AND HEMOGLOBIN AS WELL  AS
   THE  MITROPHENYL ESTf-RS  OF TY30SINE (KM = 2.4 MM), GLYCINE, TRYPTOPHAN,
   AND  PHENYLALANINE.

 AHEARN,  3.G.,  W.L. COOK,  ANO S.4.  CROW,  1931.  EFFECTS  OF  POLLUTANTS  ON
 MICRGBIAL  ACTIVITIES  IN  ESTUA3INE   SURFACE  FILMS.  EPA-600/4-81-009,  U.S.
 ENVIRONMtMTAL  PROTECTION   AGENCY,  ENVIRONMENTAL  RESEARCH  LABORATORY,  GULF
 SREEZE, FL.   20°.
 AVAIL,  FROM NTIS, SPRINGFIELD, VA:   P381-171133.

   SAMPLES  OF INSHORE SURFACE FILMS -ROM ESCAMBIA BAY, FLORIDA AND  FROM
   SITES   IM  THE NORTH SEA  YIELDED  POPULATIONS OF AEROBIC,  HETEROTROPHIC
   MICROORGANISMS  'JP TO  10 TO THE  EIGHTH POWER ML-1 OR 10 TO  THE  SIXTH
   POWE^   CM-2. HYDROCARBONOCLASTIC  ORGANISMS OCCURRED IN RELATIVELY  LOW
  • POPULATIONS. A COMPARISON OF SPECIES Of YEftSTS PREVALENT IN t^ORTH  SEA
   WATERS  BEFORE AND AFTE/?  OIL PRODUCTION ACTIVITIES INDICATED A SHIFT TO
   A  MORE  WIDESPREAD  DISTRIBUTION OF  HYDROCARBONOCLASTIC  FORMS  WITH
   POSSIBLE INHIBITION OF  A NON-HYDROCARBON UTILIZING SPECIES.
   EXAMINATION OF VARIOUS  HYDROCARBONS  AND CHLORINATED COMPOUNDS WITH THE
   POTENTIAL  OF  EEIMG SEQUESTERED  IN  NATURAL FILMS INDICATED  THAT  66%
   CCULD POTENTIALLY ALTER  MICROBIAL METABOLIC PROCESSES IN THE SLICK. IN
   MICROCOSM  STUDIES  OF   6STUARINE  SYSTEMS,  REPRESENTATIVE  COMPOUNDS
   DEMONSTRATED A SELECTIVE EFFECT  FOR  MICROFUNGI.
                                  PAGE

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AHEARN,  D.G.,  $.4.  CROW,  AND W.L. COOK,  1977.  MICROBIAL  INTERACTIONS  WITH
PESTICIDES  IN  ESTUARI1E  SJRCACE SLICKS.  PPA-500/3-77-050,  U.S.  ENVIRONMENTAL
PROTECTIOM  AGENCY,  5NVIRGNMENTAL RESEARCH LABORATORY, GULF  3R£EZE,   FL.  22P.

   ESTUARINE   SURFACE   FILl^S  FROM ESCAM6IA 6SY,  FLORIDA,  AND   ADJACENT
   WATERS   WERE   SAMPLED SY USIMG THE MEMBRANE  ADSORPTION  TECHNIQUE   TO
   ENUMERATE   MICR08IAL   POPULATIONS.  SAMPLES  OF THE  UPPER  10   MM   OF
   ESTUARINE  SURFACE FILMS YIELDED MICROBIAL POPULATIONS  UP TO 10 TO   THE
   cIGHTH   POWER   ML-1  OR  10 TO THE FIFTH POWER CM-.2.  THESE  POPULATIONS
   v^Er^E 10  TO  100  TIMES  GREATER THAN THOSE IN UNDERLYING  WATERS  OF  10  CM,
   PREDOMINANT  BACTERIA  IN SURFACE FILMS AS ISOLATED ON MARINE AGAR  WERE
   MOTILE,  N3NPIGM-CNTED,   GRAM-NEGATIVE RODS.  COLONY-FORMING   UNITS   OF
   YEASTS   AND  MOLDS ON  MYCOLOGICAL AGAR PREPARED WITH 5Q%  SEAWATER  WERE
   FOUND IN CONCENTRATIONS TO 10 TO THE FOURTH POWER ML-1 OR 28  CM-2.  THE
   PREDOMINANT   SURFACE  FILM ISOLATES FROM MARINE AGAR  WERE  PROTEQLYTIC
   AND AMYLQLYTIC  BUT  EXHIBITED ONLY WEAK TO NEGLIGIBLE
   HYDRHCAR80NOCLASTIC  ANO LIPOLYTIC ACTIVITIES. A GREATER  PROPORTION   OF
   THE  SURFACE-FILM BACTERIA, as COMPARED TO THOSE AT 10 CM DEPTH,  WERE
   CAPA3LE  OF  GROWTH DN  FRESHWATER MEDIA. WITH SELECTIVE  ISOLATION  MEDIA,
   AMYLOLYTIC,   AMD   LI°OLYTIC  BACTERIA  APPEARED  TO  COMPRISE  A  MORE
   SIGNIFICANT  PROPORTION  OF THE TOTAL POPULATION- TWENTY-ONE
   REPRESENTATIVE   BACTERIA, YEASTS, AND FILAMENTOUS FUNGI  FROM  INITIAL
   SAMPLING  OF   SURFACE  MICROLAYERS  WERE TESTED  FOR   THE  EFFECTS   OF
   SELECTED PESTICIDES  ON  UTILIZATION OF VARIOUS SUBSTRATES. ONE
   BACTERIUM   WAS   SENSITIVE TO PCB FORMULATIONS. IN  SUBSEQUENT  STUDIES
   WITH 53  ISOLATES  REPRESENTATIVE OF MORE DIVERSE PHYSIOLOGICAL  GROUPS,
   0-CHLCRQNAPHTHiLENE,   PCS 1016, AND PENTACHLQRQPHENOL  WERE  INHIBITORY
   TC  A LARGE  PORTION  OF  THE ISOLATES AND HEPTACHLOR, 8IPHENYL,  PYRENE,
   AND PC3  1016  SIGNIFICANTLY REDUCED HSXADECANE UTILIZATION.

AHEAR;J, O.G.,  S.A. CROW, N.H. BERMER, AND S.P. MEYERS.  1976.
MICROBIOLOGICAL   CYCLING  CF  OIL  IN  ESTUARINE  MARSHLANDS.  IN:   ESTUARINE
PROCESSES,  VOL.  1:  USES,  STRESSES, AND ADAPTATION TO THE ESTUARY.   MARTIN  L.
WILEY,  EDITOR,   ACADEMIC  PRESS, INC., NEW YORK,  NY.  PP.  433-492.   CERL,G8
X3044O.

   INDIGENOUS  MICRO^LDRA OF SEDIMENTS OF SPARTINA MARSHES OF THE
   LOUISIANA  COAST INCLUDE A HIGH PERCENTAGE OF CELLULOLYTIC BACTERIA  AND
   4SCC5POROGENQUS  YEASTS  ("ICHIA AMD KLUYVEROMYCES). AT  SITES   EITHER
   ACCIDENTALLY  OR EXPERIMENTALLY INUNDATED WITH CRUDE OIL, THE
   PROPORTION  OF  HYGROCAR30N-UTILIZING BACTERIA AND YEASTS  INCREASED.  THE
   MARSH SEDIMENTS CQMTAINED LQJ POPULATIONS QF HYDROCARBONOCLASTIC  FUNGI
   WITH  FEW  STRAINS SHOWING SIGNIFICANT OIL-EMULSIFYING  PROPERTIES.   IN
   CULTURE,  REPRESENTATIVE MICROORGANISMS READILY UTILIZED ALKANES  FROM
   C12  TO  CIS.  OIL  UTILIZATION BY A REPRESENTATIVE  BACTERIUM   INCREASED
   SIGNIFICANTLY  &S  INCUBATION TEMPERATURES WERE RAISED FROM 10  TO  30   C,
   HH-RFAS  YEASTS SHOWED  PEAK ACTIVITY AT 20 C. OIL UTILIZATION  BY  TEST
   MICROORGANISMS  WAS  NEGLIGIBLE AT 5 C. SEEDLING OF EXPERIMENTALLY  OILED
   MARSH PLOTS  WITH  A  MIXED CULTURE Oc CANDIDA MALTOSA AND  C.  LIPQLYTICA
   DEMONSTRATED   THAT   THESE SPECIES SURVIVED IN THE OILED  AREA  WITHOUT
   SPREADING  TO  ADJACENT SITES. IN CULTURE THESE STRAINS  GAVE SIGNIFICANT
   tMULSIFICATION   OF   CRUDE  OIL  AND UTILIZED UP  Tl  9Q5g  DF   SELECTED
   HYDROCARBONS.
                                  PAGE

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AHEARN,  O.G.,   AMD  S.A.  CROW.   1980.  YEASTS F3QM THE NORTH  SEA   AND   AMOCO
CADIZ OIL.  SOT.  MAR.   23(1) M25-12 7.  CERL,G3 XQ74).

   THE  SPECIES   AND  DENSITIES  3F  YEASTS ISOLATED FROM NORTH  SEA   WATERS
   BEFORE  ANO   AFTER  THE PRODUCTION OF OIL WERE  COMPARED.  DE3ARYOMYCES
   HANSENII  WAS   THt   PREDOMINANT SPECIES,  BUT  AFTER  OIL  PRODUCTION,
   CANDIDA GUILLIERMOMQII,  A  HYORQC4RBONOCLASTIC YEAST, WAS MORE COMMONLY
   ISOLATED  &ND   THE   FREQUENCY OF  AUREOBASIDTUM  PULLULANS  DECREASED.
   RELATIVELY  FEW  FUNGI WERE  ISOLATED FROM AMOCO  CADIZ  OIL  COLLECTED
   TWELVE  9AYS  A"TE?  THE START OF THE SPILL, THE HIGHEST DENSITIES  WERE
   OBTAINED  -ROM T1E  OIL SAMPLES  WH?N THEY WERE FIRST EMULISIFIED  IN   A
   TWEEN 30-SEAWATER  SOLUTION.  IT  IS SUGGUSTSD THAT THE HIGH
   CONCENTRATIONS  OF  AROMATICS IN THE UNWEATHERED IRANIAN  CRUOE,  WHICH
   CONSTITUTED   A30UT   HALF 0^  THE SPILLED OIL, WERE  INHIBITORY  TO  THE
   YEAST FLORA.

ALEXANDER* MARTIN,  IN PRESS. ANOMALOUS EFFECTS OF CONCENTRATION ON
3IQDEGRADATIQN   OF  ORGANIC  CHEMICALS.  AP?>L.  ENVIRON.  MICRQ8IOL.  (ERL,GB
X481).

   THt   PURPOSE  OF THIS REVIEW  IS  TO SHOW THAT ERRONEOUS CONCLUSIONS  MAY
   3E   REACHED FROM STUDIES OR  ROUTINE TESTS DONE WITH ORGANIC  CHEMICALS
   AT   THE LEVELS 0=TEN EMPLOYED FOR PREDICTING CHEMICAL FATE IN  NATURE.
   THESE  ERRORS  IN EXTRAPOLATION FROM HIGH TO LOW CONCENTRATION MAY OCCUR
   IN   ROUTINE   EVALUATIONS  OF 8I03EGREDATION,  CAREFUL  ASSESSMENTS  OF
   KINETICS   OR  THE ESTABLISHMENT  0!" PRODUCTS FORMED IN WATERS, SOILS  OR
   SEDIMENTS.

ALEXANDER,  MiRTIN.  1935.   BIODEGRADATION  OP  ORGANIC  CHEMICALS.  ENVIRON,
SCI.  t  TECHNCL.   13C2):106- 111.  (ERL,G3 X433*).

   THE  PURPOSE  3F THIS ARTICLE  IS  TO SHOW THAT ERRONEOUS CONCLUSIONS  MAY
   BE  REACHED FRO "I STUDIES  OR ROUTINE TrSTS WITH ORGANIC CHEMICALS  AT THE
   LEVELS  OFTE^J EMPLOYED FOR PREDICTING CHEMICAL FATS IN  NATURE.  THESE
   ERRORS  IN EXTRAPOLATION FROM HIGH TO LOW CONCENTRATION MAY  OCCUR  IN
   ROUTINE EVALUATIONS OF 3IODEGRADATICN, CAREFUL ASSESSMENTS OF
   KINETICS,  OR THE ESTABLISHMENT OF PRODUCTS FORMED IN WATER, SOIL,  OR
   SEDIMENTS

SGURSUIN,  A.W.,   M.A, HOOD,  AND  R.L.  GARNAS.  1977.  ARTIFICIAL  MICR03IAL
ECOSYSTEM  FOR   DETERMIMIrJG  EFFECTS AND FATE OF TOXICANTS  IN  A   SALT-MARSH
ENVIRONMENT.  IM:  DEVELOPMENTS I?J INDUSTRIAL MICROBIOLOGY, VOL. 18.  SOCIETY
FJR   INDUSTRIAL   MICROBIOLOGY,  WASHINGTON, DC.  PP.  185-191.  (ERL,G8   309).

   AN   ARTIFICIAL LABORATORY  ENVIRONMENT DESIGNED TO DETERMINE  MICR08IAL
   INTERACTIONS   '-JITH  °OLLUTANT  CHEMICALS IS PROPOSED.  THE  SYSTEM  IS
   D£3IG?siED  TO   OBTAIN  MAXIMUM SEPRODUCIBILITY  BETWEEN  REPLICATES  BY
   DIVIDING   &   SINGLE TANK P-JT3 SEPARATE CLOSED  CHAMBERS.  RAOIOLABELED
   TOXICANTS  ARE ADO~C DIRECTLY TO THE C3RE-CHAM5ERS AND  MONITORED  FOR
   METABOLIC  BREAKDOWN. FURTHER INFORMATION IS OBTAINED EASILY ON CHANGES
   IN MICR03IAL,  PHYSIOLOGICAL  INDEXES INDUCEO BY THE TOXICANTS,
   TECHNIQUES  F03  MONITORING   EFFECTS 0>c THE METHYL  PARATHION  ON  THE
   MICROBIAL  POPULATION  AND  THE  FATE  OF  THIS  CHEMICAL  ARE   GIVEN.
                                  PAGE

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B3U3QUIN,  iL W,  1984.  3IODEGR ADATIQN IN THE ESTUAR INE-HARINE  ENVIRONMENTS
AND  TH- GENETICALLY ALTERED MICROBE.  IN:  GENETIC CONTROL OF  ENVIRONMENTAL
POLLUTANTS.  GILBERT  S.  OMFMN   AND AL-XANOER  HQLLAENDER,  EDITORS,  PLENUM
PRESS, NEW YC3K, MY.  PP. 97-115.  CERL,G8 497).

   HISTORICALLY, SOMT ORGANIC AND INORGANIC COMPOUNDS HAVE SEEN
   CONSIDERED  SERIOUS  ENVIRONMENTAL  THREATS  FROM  THE  STANDPOINT  OF
   QUANTITY PRODUCED, BIO ACCUMULATION» TQXICITY, OR ADVERSE ENVIRONMENTAL
   EFFECTS. THIS PAPER DOCUMENTS  SELECTED EXAMPLES OF KNOWN INTRODUCTIONS
   JF TOXIC CHEMICALS INTO MARINE AND ESTUARINE ENVIRONMENTS AND
   DESCRI3ES  HOW  HA3ITAT DIFFERENCES AF=ECT  8IQDEGRADATION  POTENTIAL.
   CONCERNS REGARDING RELEASE OF  GENETICALLY ALTERED ORGANISMS INTO THESE
   ENVIRONMENTS ALSO ARE DISCUSSED.

oQURQUI.M, A.W,  n77.  DEGRADATION OF MALATHION BY SALT-MARSH MICROORGANISMS.
APPL. ENVIRON. .MICROBIOL.  33C2): 356-362,  CERL,GB 291),

   NUMEROUS  3ACTERIA  FROM  A  SALT-MARSH  ENVIRONMENT  ARE  CAPABLE  OF
   DEGRADING  MALATHION,  AN ORGANOPHCSPHATE INSECTICIDE,  WHEN  SUPPLIED
   WITH ADDITIONAL NUTRIENTS AS ENERGY AND CARBON SOURCES- SEVEN ISOLATES
   EXHIBITED  ABILITY (48 TO 90DO T3 DEGRADE MALATHION AS A  SOLE  CARBON
   SOURCE.  GAS AND THIN-LAYER CHROMATOGRAPHY AND  INFRARED  SPECTROSCOPY
   CONFIRMED  MALATHION TO BE DEGRADED VIA MALATHION-MQNOCARBQXYLIC  ACID
   TO  THE DICARBOXYLIC ACID AND  THEN TO VARIOUS PHOSPHOTHIONATES.  THESE
   TECHNIQUES  ALSO IDENTIFIED  CESMETHYL-MAL^THION,  PHOSPHOROTHIONATES,
   AND FOUR-C^RSG'J OICARB3X YL 1C ACIDS AS DEGRADATION PRODUCTS FORMED AS A
   RESULT 0 = ?HnS3HAT4SE ACTIVITY.

3QURQUIN, A.W,  1980.  DISCUSSION - AQUATIC MXCR03IAL ECOLOGY.   IN:
MICROBIOLOGY—1980.  DAVID SCHLcSSINGER, cOITaP» AMERICAN SOCIETY FOR
MICROBIOLOGY, WASHINGTON, DC.  PP. 390-391.  CERL,GB XI57*).

   WE  HAVE  3EEN DISCUSSING THE  PROBLEM OF HOW TQ  ASSESS  EMVIRONMENTAL
   STRESS  ON  ECOSYSTEMS  Af'iD  THE  MICROBIOLOGICAL  PROCESSES  THEREIN.
   BASICALLY,  WHAT  WE  HAVE BEEM DISCUSSING  ARE  METHODS—METHODS  FOR
   MEASURING  BIDMASS, HETEROTR1PHIC ACTIVITY, 3IODEGRADATION,  AND  OTHER
   INDICATORS  2F  ENVIRONMENTAL  QUALITY.  WHAT  I  WOULD  LIKE  TO  SEE
   DISCUSSED NCW IS THE QUESTION:  "WHAT CAN WE G:T OUT OF THESE  METHODS
   THAT  CAN 3£ USED 3Y REGULATORY AGENCIES?" I AM NOT SURE THAT  WE  ARE
   ANY  CLOSER TO AGREEMENT ON «NY PARTICULAR METHOD OR METHODS THAT  ARE
   MORE ACCEPTABLE THAN OTHERS TO THE SCIENTIFIC COMMUNITY FOR  ASSESSING
   ANY ENVIRONMENTAL STRESS. HOWEVER, I THINK THAT WE HAVE LEARNED A  LOT
   ABOUT  THE  VARI1US  METHODS,  INCLUDING THEIR  LIMITATIONS  AND  THEIR
   POSSIBLE  3ENfcFITS, WE HAVE ADDRESSED VARIOUS RESEARCH NEEDS AND  HAVE
   JUST HEARD A VERY EXCELLENT PRESENTATION OM THIS SU5JECT, WHAT I WOULD
   LIKE  TO AID Tl THIS IS A RFQUEST THAT WE BEGIN TO APPLY SOME OF  THIS
   INFORMATION, PARTICULARLY IN TERMS OF THE LIMITATIONS AND BENEFITS  OF
   THE  VARIOUS  METHODS,  TQ  ASSESS THE SO-CALLED  HEALTH  OF  A  GIVEN
   ENVIRONMENT. THERE ARE ENVIRONMENTAL DECISIONS WHICH MUST 3E BASED  ON
   THE  AVAILABLE T ECHNOLrlGY, BECAUSE WE REALLY DO NOT HAVE ANY TIME  AND
   MUST MAKE SCME DECISIONS NOW.  WE CAN MODIFY THOSE DECISIONS LATER, BUT
   A  DECISION IS NEEDED NCW EASED ON THE CURRENT TECHNOLOGY.  IF  PEOPLE
   SUCH  AS  THOSE  AT THIS CONFERENCE DO NOT AID  IN  DETERMINING  WHICH
   METHODS  SHOULD BE USED VIITH WHAT QUALIFICATIONS, THEN LESS  QUALIFIED
   PEOPLE WILL ?1AKE THOSE DECISIONS.
                                 PAGE

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BJURC'JIN, A.W.,  AND V.A. PRZY3 YSZEWSK I .   1977.   DISTRIBUTION OF BACTERIA  WITH
NITRILOTRIACEFATE-DcGSADING  POTENTIAL   IN  AN   ESTUARINE  ENVIRONMENT.  APPL.
ENVIRJN. MICPQ8IGL.  34(4 ): 411-41 8 .   CE3L,GS 323).

   ATTEMPTS TO  ISOLATE ESTUAftINc BACTZRIA CAPABLE  OF METABOLIZING
   NITRIL3TRIACETATE  CNTA)  AS A SOLE CARBON  SOURCE  FROM  AREAS  WITHIN
   ESCAAlBIA BAY,  FLA., WERE UNSUCCESSFUL; HOWEVER,  BACTERIA FROM
   FRESHWATER STREAMS AND FROM ESTUARINE  SURFACE qiCRQLAYERS WERE  EASILY
   ADAPTED TC DEGRADATION OF MTA IN FRESHWATER  MEDIUM,  A PSEUDQMONAS  SP.
   STRAIN CATCC  29600),  CAPABLE OF GROWTH IN MTA AS A SOLE CARBON SOURCE ,
   McTASOLIZEO  NTA  AT A  REDUCED RATE  IN  A SALINE MEDIUM C15PPT), COMPARED
   WITH  A  FRESHWATER  M'EDIUM CO TO  15PPT),   MICROORGANISMS  CAPABLE  OF
   DEGRADING  MTA  EXIST IN ESTUARINE  SURFACE  MICROLAYERS  AND  IN  FRESH
   SU^SUR'-ACE   WATERS  JUST  BEFORE   ENTERING   THE   ESTUARY!  THESE  DATA
   INDICATE   AN  INTERFERENCE WITH NTA  CATA80LISM 3Y SOME UNKNOWN  FACTORS
   OF  THE  ESTUARINE  ENVIRONMENT RATHER THA4  AN   ABSENCE  OF  POTENTIAL
   NTA-OE3RADIN3 BACTERIA.

BOURQUIN,  AL W., AMD S, CASSIDY.  1975.  EFFECT OF P1LYCHLORINATED  8IPHENYL
FORMULATIONS  ON  THE GROWTH GF E3TUARINE  BACTERIA,   APPL. MICROBIOL.
29(1):125-127.   CERL.GB  217).

   POLYCHLORINATED  SIPHENYL FORMULATIONS  INHIBITED  THE  GROWTH OF  CERTAIN
   •ESTUARINE  BACTERIA.  THF SENSITIVE  STRAINS,  ALTHOUGH  EXHIBITING  SOME
   SIMILAR   PHYSIOLOGICAL CHARACTERISTICS,  CONTAINED  BOTH  GRAM-POSITIVE
   AND GRAM-NEGATIVE  -BACTERIA.
         ,  A.W.,  P,H. PRITCHARO, AMD  W.R.  -MAHAFFEY.   1978.  EFFECTS OF  KEPONE
 u^   EST'JAHINE MICROORGANISMS.  IN:   DEVELOPMENTS IN INDUSTRIAL  MICROBIOLOGY,
 VOL.  19.   SOCIETY FOR INDUSTRIAL  MICROBIOLOGY,  WASHINGTON, DC.  PP.  489-497.
 (ERL,GB  345).

    LQiJ   C3NCN  OF  TH= IKSECTICIDt  KEPCNE,   APPROACHING  THOSE  FOUND  IN
    CONTAMINATED  J4MES RIV-2R SEDIMENT,  WERE  SHOWN TO 8E INHIBITORY TO  THE
    GROWTH   AND  OXYGEN UPTAKE Oc  MICROORGANISMS  RANDOMLY  SELECTED  FROM
    ESTUARINE ENVIRONMENTS. NO SIGNIFICANT CORRELATIONS WERE NOTED BETWEEN
    GROWTH  INHIBITION 3Y KEPONE AND  CELL  MORPHOLOGY, ALIPHATIC HYDROCARBON
    UTILIZATIOM,  PESTICIDE TOLERANCE,  SELECTED ENZYME ACTIVITIES,  NITRATE
    REDUCTION,  AND UREA HYDROLYSIS,  OXYGEN  UPTAKE BY PURE CULTURES  GROWN
    ON  GLUCOSE OR HYDROCARBONS AT CELL DENSITIES EQUIVALENT TO 10 TO  THE
    THIRD   P1WER   THRU 10 TO THE FOURTH POWER CELLS/ML  WAS  DECREASED  BY
    60-100? AT K£P?NE CCNCN DF 0.02-2.0 MG/LIT-ER. TOTAL VIABLE COUNTS FROM
    ESTUARINE WATER 3R SEDIMENTS GROWN  AEROBICALLY ON 4GAR MEDIA
    CONTAINING 0.02 MG/LIT£R KEPONE  WERE  REDUCED BY  8-78?. THE  INHIBITORY
    EFFECT   WAS ELIMINATED PARTIALLY  WHEN  SEDIMENT POPULATIONS WERE  GROWN
    ANAER03ICALLY.
                                   PAGE

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BOURQUIM, A.M.   1977.   EFFECTS 'JF MALATHION  OM  MICROORG ANISMS OF AN
ARTIFICIAL  SALT-M4RSH  ENVIRONMENT.  J.  ENVIRON.  G'JAL.   6(4): 373-378.  C£RL,GB
312).

   LA3CRAT.OQY   SALT-MARSH  ENVIRONMENTS  HERE  TREATED  WITH  MALATHION,  AN
   ORGANOPHOSPHATE  INSECTICIDE, AND  AERQ3IC  HETEROTROPHJC BACTERIA  WERE
   MONITORED   T3  DETERMINE CHANGES IN  THEIR  MICROBIAL  ECOLOGY.  SEVERAL
   PHYSIOLOGICAL  ACTIVITIES WERE ASSAYED  IN  BOTH  TREATED  AND  UNTREATED
   CONTROLS;  HOWEVER,  NO RELIABLE TRENDS IN  NUMBERS  OF THESE
   MICROORGANISMS   W63E  DETECTED.  ON  THE   OTHER  HAND,   POPULATIONS  OF
   MALATHION  SOLE-CAR30N-OEGRADIN3 BACTERIA  INCREASED  SIGNIFICANTLY  WITH
   INCREASING   TREATMENT  LEVEL>  AMD   IN   THE   SEDIMENTS  WITH  REPEATED
   TREATMENT.   MALATHION COMFTA80LI2ING  BACTERIA INCREASED  SIGNIFICANTLY
   OVER  THE CONTROL SYSTEMS IN  TH5 WATER COLUMN  WITH  INCREASING TREATMENT
   LEVELS.   ALTHOUGH  NUMBERS OF MALATHIO-N-3EGR ADING   BACTERIA  INCREASED
   WITH  HIGHF1  TREATMENT LEVELS OR FREQUENCY  OF  TREATMENT, THESE  CHANGES
   HAD   NO  EFFECT  OM THE CUMBERS OF BACTERIA  FROM  THE  WATER OR  SEDIMENT.
   WHEN   AN  OR3AMOCHLCPINE  INSECTICIDE,  MIRSX, WAS  USED  TO  TREAT  THE
   ECOSYSTEMS,   ESSENTIALLY NO CHANGES  IK  THE BACTERIAL POPULATIONS  WERE
   DETcCTED,

 30URQUIN,   A.W.  1973.  ESTUARINE MICROBES  AND  ORGANOCHLORINE  PESTICIDES  
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BOURQUIN,  AL   W.   1973.   IMpaCT OF MICR03IAL S?EO CULTURES   IN   THE   AQUATIC
ENVIRONMENT.   IN:   PROCEEDINGS OF THE FIRST MICROBIOLOGY  SEMINAR  ON
STANDARDIZATION   OF  METHHDS.  EPA-R4-73-022, U.S.  ENVIRONMENTAL  PROTECTION
AGENCY, WASHINGTON,  DC.   PP.  140-142.  (E*L,G3 203*).

   MICRGBIAL SEED  CULTURES ARE CURRENTLY 3EING STUDIED FOR APPLICATION  TO
   THE  ENVIRONMENT  4S   MICROBIOLOGICAL PESTICIDES.  VIRUSES  HAVE   BEEN
   ISOLATED  WHICH ATTACK SELECTIVELY THE CABBAGE BOLL5 A  BACTERIUM   HAS
   BEEN ISOLATED  AS A SPECIFIC PATHOGEN OF MOSQUITOES; AND CHITINOCLASTIC
   BACTERIA  HAVE   3F£N   PROPOSED AS AGENTS AGAINST  PLANT  PREDATORS   IN
   ESTUARINc   AREAS.   THE RANGE 0" IMPACT ON THE AQUATIC  ENVIRONMENT   BY
   SE--D CJLTUQES  MUST BE  INVESTIGATED ADEQUATELY BEFORE THEY  ARE  USED   ON
   A LARGE SC:>L5,

30URQUINi»  A.VI.,  S.P. MEY'ERS, AND D.G. AHEARN,  1975.  IMPACT OF  THS   USE   OF
MICROORGANISMS ON  THE AQUATIC ENVIRONMENT.  EPA-660/3-75-001, U.S.
ENVIRONMENTAL   PROTECTION  AGtNCY, NATIONAL  ENVIRONMENTAL  RESEARCH   CENTER,
CJRVALLIS, OR.   259?.  CE3L,GB 235*).
AVAIL. FROM  NTIS,  S3RIN3FIELO, VA:  P3-240 159,

   THIS REPORT CONTAINS  THE PROCEEDINGS OF A SYMPOSIUM-WORKSHOP SPONSORED
   3Y THE EPA  GJLF BREEZE ENVIRONMENTAL RESEARCH LABORATORY TO  DETERMINE
   THE  P2SSI3LE   IMPACT   0-  ARTICICI4LLY  INTRODUCING  MICROBIAL  INSECT
   CONTROL   AGENTS OR OIL-DEGRADING AGENTS INTO THE AQUATIC   ENVIRONMENT.
   THE EFFICACY  AND SAFETY TESTING, ESPECIALLY AGAINST NON-TARGET AQUATIC
   ORGANISMS,   FOR  USE   OF BACTERIA, VIURSES,  FUNGI,  AND   PROTOZOA   TO
   CONTROL   AQUATIC  INSECT  PESTS IS DISCUSSED  WITH  REMARKS  OF  PANEL
   MEMBERS   REPRESENTING   GOVERNMENT,  ACAOEMIA,  AND  INDUSTRY.  SPECIAL
   ATTENTION IS  GIVEN TO  PERSISTENCE 3F PATHOGENS IN AQUATIC  ENVIRONMENTS
   AS  *'ELL  AS CONTROL OF AQUATIC WEEDS AND OTHER NON-INSECT  PESTS.  THE
   USE  CF MICROORGANISMS TO  CLEAN UP OIL SPILLS IN AQUATIC   ENVIRONMENTS
   IS  OISCUSSEO   BY INDUSTRIAL, ACADEMIC, AND  GOVERNMENTAL  SCIENTISTS.
   SPECIAL   CONSIDERATIONS ARE GIVEN TO SELECTION OF  HYDROCARBONOCLASTIC
   MICROORGANISMS  AND USE OF  THESE MICROORGANISMS IN SPECIAL
   ENVIRONMENTS—ARCTIC   REGIONS  AND  LOUISIANA  SALT  MARSHES,  SUMMARY
   PAPERS ARE  PRESENTED  FOR EACH PANEL CONCERNED WITH MICROBIAL
   PESTICIDES  AND  ONE SUMMARY FOR THE SESSION ON MICROBIAL DEGRADATION  OF
   OIL.   EXCELLENT  BIBLIOGRAPHIES  ARE PRESENTED  WITH   EACH  PAPER   AND
   DISCUSSION.

30URQUIN,  A.W.,  L.A. KIEFER, N.H. 8ERN-ER, S. CROW, AMD   D.G.  AHEARN.   1975.
INHIBITION   OF  ESTUARINE MICROORGANISMS 3Y  POLYCHLO>:?INATEO  BIPHENYLS.   IN:
DEVELOPMENT  IN   INDUSTRIAL  MICROBIOLOGY, VOL,  16,  AMERICAN  INSTITUTE   OF
BIOLOGICAL SCIENCES,  WASHINGTON, OC.  P*». 256-251.  (ERL,GB 230).

   OVER 100  ISOLATES OF  REPRESENTATIVE ESTUARINE BACTERIA AND FUNGI   WERE
   SCREENED  FC«   THEIR   ABILITY TO G^OW IN THE  PRESENCE  OF  COMMERCIAL
   PREPARATIONS   OF  POLYCHLCRINATEO  EIPHENYLS  CPCB).   SUPER  ABSORBANT
   SENSITIVITY DISCS IMPREGNATED WITH UP TO 0.5 MG OF PCB WERE PLACED   ON
   THE  SURFACE  0^ FRiSHLY INOCULATED SOLID MEDIA.  TWENTY-SIX  BACTERIA,
   REPRESENTING   BOTH GRAM-POSITIVE AND GRAM-NEGATIVE STRAINS OF  VARYING
   MORPHOLOGY, SHOWED VARYING DEGREES OF SENSITIVITY TO PCB,  IN   CONTRAST
   TC INSENSITIVE  ISOLATES, SENSITIVE STRAINS WERE MAINLY AMYLOLYTIC   AND
   PROT50LYTIC.   PC6  HAD NtGLIGIBLE EFFECT ON TH5 GROWTH 0?  FUNGI.   THE
   SENSITIVITY OF  SELECT  CULTURES OF HFT€ ROTR-3PHIC BACTERIA TO PC3  MAY BE
   OF CONSIDERABLE IMPORTANCE TO NUTRIENT TURNOVER IN ESTUARINE
   ECOSYSTEMS.
                                  PAGE

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c
BOURQUIN,  A.M.,  R.L.  GARNASt  D.H.  PRITCHARD, C.G. WILKES, C.R.  CRIPE,   AND
N.I.  RUBINSTEIN.   1979.   INTERDEPENDENT  MICROCOSMS ^OR  THE  ASSESSMENT   OF
POLLUTANTS IN THE MARINE  ENVIRONMENT.   INT. J. ENVIRON. STUD.  13C2):131-140.
CHRLfGB 348).

   LABORATORY MICROCOSMS  ARE  DESCRIBED FOX ASSESSING TH~ FATE AND EFFECTS
   OF  POLLUTANTS   IN  MARINE  AND  ESTUARINE  ENVIRONMENTS.   THESE  SYSTEMS
    OCUS  ON  SPECIFIC   ECOSYSTEM  PROCESSES  AND  INTERACTIONS  AND  ARE
   INTERDEPENDENT IN  THAT  THE RESULTS  OF ALL ARE NECESSARY F03 A COMPLETE
   DESCRIPTION  0-  A   POLLUTANT'S ENVIRONMENTAL  IMPACT.   THE  FOLLOWING
   INDIVIDUAL   SYSTEMS   ARE   DESCRIBED  USING  METHYL  PARATHION  AS  THE
   POLLUTANT: ENVIRONMENTAL  FATE  SCREWING SYSTEM; ECO-CORE SYSTEM;
   CONTINUOUS   FLOW SYSTEMS;  AQUATIC GRADIENT AVOIDANCE RESPONSE  SYSTEM;
   3ENFHIC 3IOASSAY SYSTEM.

BQURQUIN,  AL   U.,  AND DAVID  T.  GI3SON.  1373.  MICROBIAL  DEGRADATION   OF
HALQGENATED  HYDROCARBONS.   IN:   WATER  CHL3RINATION:  cNVIRDNMENTAL IMPACT  AND
HEALTH   EFFcCTS,  VOL.  2,   ROBERT L, JOLLEY, HEND GORCHEV,  AND  HAMILTON   0.
HfcYWARD,  JR.,  EDITORS,  ANN  ARBOR SCIENCE PUBLISHERS*  ANN  ARBOR,  MI.   PP.
253-264.  <£RL,G8 361).


BOURQUIN, AL U.>  JI1  C. SPAIN,  AND P.H. PRITCHARD.  1982.   MICROBIAL
DEGRADATION  OF  XENOBIOTIC COMPOUNDS,  IN:  PROCEEDINGS OF  THE TWELFTH
CONFERENCE   ON  ENVIRONMENTAL  TOXICOLOGY 3, 4, AND 5 NOVEMBER  1981,  CDAYTON,
OH).   AEROSPACE  RESEARCH  LABS.,  WRIGHT-PATTERSON  AFB,   OH.  PP.  354-369.
C=RL»GB  437*).

    MICROBIAL DEGRADATION  IN NATURAL  ENVIRONMENTS IS PROBABLY  THE  MOST
    DIFFICULT "ATE DROCFSS TO  STUDY AND QUANTITATE. INFORMATION  NECESSARY
    TO  PREDICT  3IOPEGRADATION OF  fl CHEMICAL DEPENDS ON LAWS OF  CHEMISTRY
    AND   THE   '^EMETIC  CAPA3ILITIES OF THE MICROBIAL POPULATIONS.  WE  HAVE
    PRODUCED, IN  2UR  LABORATORY,  SEVERAL CASE STUDIES ON  DEGRADATION  OF
    SELECTED  TOXICANTS  UNDfcR  CONDITIONS THAT MAINTAIN COMPLEXITIES OF  THE
    NATURAL   ENVIRONMENT  AND   ASSOCIATED  MICROORGANISMS.   3IODEGRADATIQN
    STUDIES   WITH  NTA  DEMONSTRATED THIS NORMALLY  BIODEGRADABLE  COMPOUND
    PERSISTS   IN ESTUARINE ENVIRONHE^TS AND INDICATE COMPLEX  INTERACTIONS
    IN  NATURAL ENVIRONMENTS WHICH  COMPLICATE CUR UMDHRSTANDING OF
    BIODEG8AOATI-3N   MECHANISMS.  INTERACTION WITH ENVIRONMENTAL  CONDITIONS
    OR  LACK DF GENETIC  CAPABILITIES WITHIN AN ENVIRONMENT WAS  DEMOSTRATED
    FURTHER WHEN P«ESHMATER,  BUT NOT SALTWATER, MICROBIAL POPULATIONS WERE
    SHOWN  TO ADA»T  WITHIN SEVERAL DAYS TO DEGRADE  P-NITOPHENOL  RAPIDLY.
    DIFFERENCES  I*! CHEMICAL STRUCTURE AFFECT DEGRADATION OF TOXIC
    CHEMICALS IN  NATURAL MrDIA WITH MIXED  MICR03IAL  POPULATIONS.  SUCH
    STRUCTURES RAN^E FROM COMPOUND'S LIKE METHYL PARATHION,  WHICH
    COMPLETELY   DEGRADES,  TO  DIMILIN, WHICH PARTIALLY DEGRADES AND  YIELDS
    NCMBIQDEGRACABLE PRODUCTS, TD  KEPONE, WHICH DOES NOT DEGRADE.
                               PAGE

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.
BQURQUIN, AL W.   1975.   MICR03IAL-MALATHION INTERACTION IM ARTIFICIAL
SALT-MARSH EC'JSYSTE MS— EFFECT AND DEGRADATION.  EPA-660/3-75-03 5 , U.S
ENVIRONMENTAL   PROTECTION   AGENCY, NATIONAL  ENVIRONMENTAL  RESEARCH  CENTER,
CORVALLIS, 3R.   40P.   (ERL.GB 236*).

   MALATHICN   IS   RAPIDLY   DEGRADED IN VITRO 3Y  SALT-MARSH  BACTERIA  TO
   MALATHIQN-MONQCARBQXYLIC ACID, MALATHION-DICARBOXYLIC ACID AND VARIOUS
   PHQSPHOTHIONATES AS A RESULT OF CARBOXYESTERASE CLEAVAGE. IN ADDITION,
   SOME  EXPECTED  PHQSPHATASE ACTIVITY PRODUCES DESMETHYL-MALATHlQN ,
   PHOSPMDTIOMATSSi  4-CAR80N OICARBGXYLIC ACIDS, AND CORRESPONDING  ETHYL
   ESTERS.   IM A  SIMULATED SALT-MARSH ENVIRONMENT, MALATHION IS  DEGRADED
   3Y THE INDIGENOUS BACTERIAL COMMUNITY. NUMBERS OF 3ACTERIA CAPABLE  OF
   DEGRADING   MALATHION  IN THE PRESENCE Of ADDITIONAL NUTRIENTS  INCREASE
   IN   THE SEOIMEMTS WITH  INCREASING FREQUENCY OF APPLICATION AND IN  THE
   WATER COLUMN  WITH  THE INCREASING LEVEL  OF  TREATMENT.  NUMBERS  OF
   BACTZRIA  WHICH DEGRADE  MALATHION AS A SOLE CARBON SOURCE ARE LINKED TO
   THE  LEVEL  OF TREATMENT  IN SEDIMENTS AND THE FREQUENCY OF TREATMENT  IN
   THE   WATER   COLUMN; HOWEVER, THESE BACTERIA 00 NOT APPEAR  TO  PLAY  A
   SIGNIFICANT  ROLE  IN  THE DISSIPATION OF MALATHION.  I  BELIEVE  THAT
   FRE<*UEMCY  OF T3£iTv!ENT, INCREASES NUMBERS OF MALATHION CO-METABOLIZING
   BACTERIA   WHICH  CATALYZE A MORE RAPID DISSIPATION  OF  THE  COMPOUND,
   WHICH  RESULTS  IN FEWER SOLS CARSON DEGRADERS. THE  DISAPPEARANCE  OF
   MALATHION  IN THE SALT-MARSH ENVIRONMENT IS INFLUENCED BY BOTH CHEMICAL
   AND   BIOLOGICAL DEGRADATION; HOWEVER, 4T TEMPERATURES 3ELOW 26  C  AND
   SALINITIES   3ELOW  20 0/00, CHEMICAL MECHANISMS APPEAR TO BE  OF  LESS
   IMPORTANCE  THAN BIOLOGICAL DEGRADATION.
                                   PAGE

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BOURQUIN,  4.W.*  AND  D.G.   AHF.ARN.   1976.   MICROBIOLOGY   AND   CHEMISTRY   OF
ESTUARIME SURFACE MICROLA Y ESS.   IM:   PROCEEDINGS  OF  THE  INTERNATIONAL
SYMPOSIUM OH  1AR1ME POLLUTION RESEARCH.   CP4-800/9-76-032,  SAMUCL  P.   MEYERS,
EDITOR, U.S. ENVIRONMENTAL  PROTECTION  AGENCY,  ENVIRONMENTAL  RESEARCH
LABORATORY, GUL= 3REE7.E,  ?L.   PP.  89-36.   (ERL.-3B  313*).

   ORGANIC MICROL4YEP5 QCCUR  AT  THE  AIR-WATER  INTERFACE  OF  MOST  BODIES OF
   WATER.  TH>:  MICROL4YER  OR  "SEA  SLICK"  FORMATION APPEARS  TO BE   RELATED
   MAINLY  TO DECAY QP NATURALLY OCCURRING  AQUATIC ORGANISMS OR  TO  THEIR
   PRODUCTION   3F  LIPODIAL  bY-PRQDUCTS  (BABKOV,  1965).   SEA  SLICKS   ARE
   KNOWN  TO  INFLUENCE   WAVE ACTION  4ND   HEIGHT,  AIR-WATER  TEMPERATURE
   EXCHANGE,  STABILITY   OF  BUBBLES  AMD  FOAMS,  AND THE   CONCENTRATION   OF
   SALT-C3NTAINING MICRO-DROPLETS  IN  THE  MARINE ATMOSPHERE  CBAIER,  1970).
   IN  COASTAL  RESIGNS PARTICULARLY,  THS  DIRECT ACTIVITIES  OF MAN  ARE   OF
   INCREASING IMPORTANCE  IN  THE  GENERATION  OF  SURFACE SLICKS.  INDUSTRIAL
   AND  MJNICIPU SEWAGE  EFFLUENTS CONSTITUTE  THE  MAJOR  SOURCE   OF  FILMS
   AND FCAMS, BUT CRUDE OIL  SPILLAGE  APPEARS  TO BE A MAJOR  CONTRIBUTOR IN
   LOCALIZED AREAS (AHEARN,  1974). IN  STUDIES  FROM OUR LABORATORIES ON  A
   YEAST ISOL&TED FRO
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BOURQ'JIN,  AL W.,  P.H.  PRITCHAR3, WILLIAM H. *ALK=R, AND ROD   PARISH.   1985.
PROCEEDINGS 0= THE  WORKSHOP:  BIODEGPADATION KINETICS NAVARRE  8>=ACH,   FLORIDA
18-20 OCTOBER 1983.   EPA/600/3-85/018, U.S. ENVIRONMENTAL PROTECTION   AGENCY,
ENVIRONMENTAL P-SEARCH  LABORATORY, GULF BREEZE, FL.  161P.
   THIS WORKSHOP,  HELD OCTOBER 18-20, 1983, AT PENSACOL4 BEACH,   FLORIDA,
   FOCUStD ON  PERTINENT ISSUES RELATED TO THE SCIENTIFIC INVESTIGATION  OF
   TH=  MICRQ3IAL   DEGRADATION  RATES OF  ORGANIC  CHEMICALS  IN  NATURAL
   ENVIRONMENTS,   PARTICIPANTS DISCUSSED METHODOLOGICAL CRITERIA  FOR
   THESE  INVESTIGATIONS  AND THE NEED FOR CONCENTRATING ON  TH6  KINETIC
   ASPECTS OF  BIO-DEGRADATION.  POSITION PAPERS DEALING WITH THE FOLLOWING
   TOPICS WERE PRESENTED IN OPEN SESSIONS:   DEGRADATION METHODOLOGY;   AND  (6)
   PERSISTENC-  AMD  EXTRAPOLATION. DISCUSSIONS WITHIN EACH  SESSION  ARE
   PRESENTED.   TH^SS  PROCEEDINGS  CONCLUDE WITH  A  SUMMARY  REPORT  AND
   WORKSHOP   CONSENSUS  REPORTS  DRAFTED  BY  SPECIAL  TASK  GROUPS   WITH
   RECOMMENDATIONS CONCERNING THE RESEARCH, PRODUCTION, AND REGULATION  OF
   POTENTIAL AQUATIC POLLUTANTS.
                                   PAGE   11

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CABELLI,  VICTOS   J.,  ANGELO r. CARLUCCI, CAROL D.  LITCHFICLD,  THEODORE   G.
METCALF, ROBERT A.  MURCHELANO, ?.H. PRITCriASD, AND STANLEY W.  WATSON.   1979.
MICROORGANISMS.   IN:   PROCEEDINGS 0* A WORKSHOP DM SCIENTIFIC  PROBLEMS
RELATING  TO  QCE4N  POLLUTION,  5STES PARK,  CO.,  JULY  10-14,   1978.   U.S.
NAH2!JJhr.P-EaNIC   AND  ATMOSPH=KIC  ADMINISTRATION,  ENVIRONMENTAL   RESEARCH
LABORATORIES, SOULDER, CO,   PP. 104-129.  CERL.SB X115*).

   THE  MICR03IAL   CLORA  NATIVE  TO OR CARRIED  INTO  MOST  COASTAL  AND
   ESTUARINE WATE'RS AND THEIR UNDERLYING SEDIMENTS GENERALLY IS EXTENSIVE
   IN BIO'IASS,  NUMBER  OF SPECIES INVOLVED, AND DIVERSITY OF PHYSIOLOGICAL
   AND  ENZYMATIC   FUNCTIONS  THEY  PERFORM.  THESE  MICROORGANISMS   PLAY
   SEVERAL  ROLES   IN  MARINE ECOSYSTEMS AND IN HUMAN USE  OF   THE  MARINE
   ENVIRONMENT  AS A  SOURCE Oc FOOD AND RECREATION. THEY MAY FUNCTION  AS
   THE  FALLOWING:   CD AGENTS OF HUMAN DISEASE THAT ARE INTRODUCED   INTO
   THE  MARINE  ,-fATERS  FROM HUMAN AND LOWER ANIMAL WASTES AND   TERRESTRIAL
   ENVIRQNEMTS  OR  THAT INCREASE IN NUMBERS THEREIN BECAUSE OF  NUTRIENT OR
   THERMAL  POLLUTION.  (2)  AGENTS OF FAUNAL  DISEASE.  C3)   SOURCES  OR
   MEDIATORS OF FOOD  TO HIGHER ORGANISMS 3Y THE DEGRADATION,
   TRANSFORMATION,   AND ASSIMILATION OF NUTRIENTS THAT  OCCUR  NATURALLY,
   TH^T  ARE TRANSPORTED INTO MARINE WATERS THROUGH TERRESTRIAL  RUN-OFF,
   OR THAT  ARE  INTRODUCED EY HUMAN ACTIVITIES, (4) DEGRADERS OR
   TRANSFORMERS   OF  POLLUTANTS SUCH AS PESTICIDES,  PETROLEUM  PRODUCTS,
   SNYTHETIC  ORG4NICS, AND METALLIC IONS LIKE MERCURY. THE  RELATIONSHIP
   OF  THE  POLLUTANT  TO THE MICRQ3IAL FLORA IS DIFFERENT IN EACH  OF  THE
   FOUR  FUNCTIONS.  < 1) WITH REFERENCE TO AGENTS OF HUMAN  DISEASE,  THE
   MICROORGANISM  ITSELF IS GENERALLY THE CONTAMINANT INTRODUCED INTO  THE
   ENVIRONMENT  USUALLY  3Y SEWAGE EFFLUENTS. (2) IN -AUNAL  DISEASE,  AN
   EXTRINSIC POLLUTANT AFFECTS A BASICALLY INTRINSIC HOST-PARASITE
   RtLATIDNSHIP   BY  STRESSING ANIMALS SO THAT  THEIR  SUSCEPTIBILITY  TO
   DISEASE  INCREASES.  (3) THE EXTERNALLY INTRODUCED ORGANIC POLLUTANT  IS
   THE  TARGET  FOR  MARINE  ORGANISMS THAT  ARE  CAPABLE  OF  DEGRADING,
   TRANSFORMING OR ASSIMILATING SUCH MATERIALS AS P-ETROLEUM  HYDROCARBONS
   AND  PESTICIDES.  C4) CONVERSELY, THE MICROBIAL  FLORA  NECESSARY  FOR
   NUTRItMT  TRANSFORMATIONS IN MARINE ECOSYSTEMS MAY THEMSELVES  BE  THE
   TARGETS  POR  THESE  ANO 3THE3 ORGANIC AND INORGANIC, EXTERNALLY
   INTRODUCED POLLUTANTS. ALTERNATIVELY, THE PROLIFERATION OF
   HETEROTROPHIC   MICROORGANISMS  UNDER  NUTRIENT  STIMULATION  CAN   HAVE
   ADVERSE  EFFECTS SUCH AS ANOXIA. ASSOCIATION, IF NOT CAUSALITY, BETWEEN
   A  FORM  OF POLLUTION AND SOME DETRIMENTAL EFFECT IS STRONG  ENOUGH  IN
   SOME INSTANCES  TO  SUPPORT CRITERIA, GUIDELINES, ANO STANDARDS AS   WELL
   AS MONITORING  PROGRAMS. SUCH IS THE CASE WITH HUMAN HEALTH  EFFECTS AND
   TO  A LESSER EXTENT CAUNAL DISEASE. NEVERTHELESS, THERE IS  A  CRITICAL
   NEED FOR ADDITIONAL EPIDFMIOLOSICAL OR EPIZOOLOGICAL DATA,  INFORMATION
   ASSOCIATING  POLLUTION  LEVELS WITH HUMAN AND FAUNAL DISEASE  AND  THE
   DENSITIES  0=   THE   ETICLCGICAL  AGENTS  INVOLVED,  AND  RESEAARCH  ON
   METHODOLOGY  (ESPECIALLY AS RELATED TO FAUNAL DISEASE). THERE IS ALSO  A
   CRITICAL  NE=D   FOR  DATA CONCERNING THE ROLES  OF  MICROORGANISMS  IN
   MARINE   ECOSYSTEMS  AND DOCUMENTING ANY EFFECTS OF POLLUTANTS ON  THEIR
   ACTIVITIES.
                                  PAGE  12

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CERNIGLIA,  CARL  E.f J3S5PH C. MORGAN,  AND  DAVID I.   GIBSON,  1979.  BACTERIAL
AND FUNGAL  OXIDATION OF OIBENZOFURAN.   BIOCHEM.  J.   180 CD : 175-185 .  CERL.GB
X03 7v).

   CUNNIN3HAMELLA  ELCGANS  AND A  MUTANT  STRAIN O8/36)  OF  3EIJERINCKIA
   BOTH   OXIDIZED OIBEN7.Q-URAU TO   2 , 3-DIHYOROXY-2 , 3-9IHYDRQDIBENZOFURAN.
   THc  BACTERIAL METABOLITE  WAS  EXTREMELY UNSTABLE  AND, IN THE  PRESENCE
   OF ACID,  W4S  RAPIDLY CONVERTED  INTO A  MIXTJR= OF  2- ANO
   3-HYDRJXYDIBcN*QFURAN. IN  COMTRAST, THE 2,3-DIHYOR1XY-2,3-OIHYDRODIBENZ
   QFURAN   FORMED  BY  C.  SLOGANS WAS STABLE  AND  DNLY  YIELDED  2-  AMD
   3-HYDR3XYDI6'ENZC=URA;g WHEN HEATED  UMOER ACIDIC CONDITIONS. THE RESULTS
   SUGGEST   THAT  BfIJERINCKIA 38/36  AND  C.  ELE3ANS  FORM  THE  RESPECTIVE
   CIS-   AND  TRAMS-ISCMERS Or 2,3-DIHYDRHOIBENZOFURAN. C.  ELEGANS  ALSO
   3XIOIZ5C OIBENZOt-URAN TO 2- Af!0 3-HYDROXYDI8EN20FURAN UNDER CONDITIONS
   THAT W3ULD NOT LEAD TO THE DEHYDRATION  OF THS TRANS-DIHYDRDDIOL. THESE
   OBSERVATIONS  IMPLICATE TlE INITIAL  FORMATIDN OF
   DIBENZ3FURAN-2,3-cPOXIDE   IN   THE  -UNGAL  OXIDATION  OF  DIBENZOFURAN.
   3EIJSRINCKIA   B8/36 ALSO PRCOUCED  A SECOND  UNSTABLE  DIHYDPQDIQL  THAT
   WAS TENTATIVELY IDENTIFIED AS  CIS~l,2-DIHYOROXY-l,2-DIHYORODIBENZOFURAN
   .   THIS  COMPOUND GAVE 2-HYDR.1XYDIBENZOFURAN AS THE   MAJOR  DEHYDRATION
   PR3DUCT   AMD   THE CIS RELATIVE  STEREOCHEMISTRY WAS   SUGGESTED  BY  THE
   IS3LATIG;]  AND  CHARACTERIZATION OF AN   ISQPROPYLIDINE  DERIVATIVE.  A
   PREPARATION  OF  CIS-NAPHTHALENE DIHYDRODIDL  DEHYDROGENASE  AND  CELL
   EXTRACTS OF THE ?ARENT STRAIN  OF BEIJERINCKI4 OXIDIZED BOTH  BACTERIAL
   DIHYDRuDIOLS   TO  CATECHOLS.  CELL  EXTRACTS  PREPARED  FROM  C.  ELEGANS
   CATALYSED AN  ANALOGOUS OXIDATION OF TRANS-2,3-DIHYOROXY-2,3-DIHYDRODIBE
   NZOFURAN  TO   '1,3-DIHYDROXYDlBENZOFURAN. THE LATTER PRODUCT  WAS  ALSO
   ISOLATED  ANO IDENTIFIED FROM  CULTURE  FILTRATES.  THE  RESULTS  SUGGEST
   THAT   BACTERIA  AMD  FUNGI UTILIZE DIFFERENT  MECHANISMS TO INITIATE  THE
   OXIDATION OF  OIBENZOFURAN.

 CcRNIGLIA,   CARL £., RICHARD  L.  HEBERT, ROBERT H. DODGE, PAUL  J.  SZANISZLO,
 AiiD  DAVID T. GIBSON,   1979.   SOME  APPROACHES TO STUDIES ON THE DEGRADATION OF
 AROMATIC  nYDROCAR30NS  BY FUNGI.   IN:   MICR03IAL DEGRADATION OF POLLUTANTS  IN
 MARINC   ENVIRONMENTS.  EPA-600/9-79-012,   AL  BOURQUIN  AMD  P.H.  PRITCHARO,
 EDITORS,  'J.S. ENVIRONMENTAL PROTECTION AGENCY, F.NVIRONMENTAL RESEARCH
 LABORATORY, GULF 3R5EZE, FL.  P?.  360-369.  (ERL,GB X214*>.

   A  WIDE   TAXONQHIC  AND PHYLOGENETIC SPECTRUM OF FUNGI  WERE  SHOWN  TO
   TRSN5F3RM NAPHTHALENE. THE ABILITY TO  OXIDIZE NAPHTHALENE PREDOMINATED
   IN   THC   MUCDRALFSf   BUT SIGNIFICANT HYDROXYLATION  ALSO  OCCURRED  IN
   SPECIES   OF  NEUROSPORA,   CLAVICEPS  AND  PSILOCYBE.  THE  PREDOMINANT
   META30LITE   CORMED  WAS  1-NAPHTHOL. OTHER   PRODUCTS  IDENTIFIED  WERE
   ^-HYOR3XY-1-T£TRALON:» T RANS-1»2-DIHYDROXY-l ,2-OIHYD'^ONAPHTHALENE,
   2-JAPHTHOL,  1,2- AMD  1,4-NAPHTHOQUINQNE. CUNNINGHAMELLA ELEGANS
   OXIDIZED  NAPHTHALENE,' BIPHENYL 4NO DI3ENZQFURAN BY REACTIONS  SIMILAR
   TO  THOSE .OBSERVED WITH MAMMALIAN ENZYME SYSTEMS-
                                   PAGE

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CLEVELAND,  MARY   ELIZABETH.  1983.  SIGTIC   AND   ASIATIC   FACTORS  AFFECTING
SORPTION  OF TOXIC COMPOUNDS TO NATURAL SEDTM^S.   *.l,   THES™   UN^R Jl?Y
OF WEST FLORIDA,  oENS4COLA, FL.  95?.  CE*L,G3  495*).
      .Tnn.                  KEPONE,  OURS3AN,   OIMILIN   AND  METHYL
   PAKATHION   (MRS)   WAS  OBSERVEJ   IH   STERILE   AND   NONSTFRILE   AQUATIC
   SEDIMENT   SYSTEMS TO ADDRESS THREE ASSUMPTIONS  IMPLICIT  IN  THE USE  OF
   PARTITION  COEFFICIENT AS A DESCRIPTOR  OF  EQUILIBRIUM   ADSORPTION:   (1)
   aDSORPTIDN  KINETICS  ARE  RAPID  AND  THESFQRE  UNIMPORTANT   TO  PATE
   CONSIDERATIONS;   c?) ADSORPTION EQUILIBRIUM  is  INDEPENDENT  OF   INITIAL
   COMPOUND   OR SOLIDS CONCENTRATIONS;  AND  (3)  ADSORPTION is   REVERSIBLE,
   ADSORPTION WAS TWO-STEPPED. AN INITIAL RAPID  PHASE  ACCOUNTED  FOR  MOST
   OF  TH.  TOTAL ADSORPTION, SUGGESTING  THAT  KINETICS  ARE UNIMPORTANT  TO
   EXPOSURE   CONCENTRATION  PREDICTIONS.  AN  INVERSE  RELATIONSHIP   BETWEEN
   PARTITION  COEFFICIENT AND SEDIMENT CONCENTRATION WAS  OBSERVED,
   INDICATING THAT 
-------
CONNOLLY, JOHN  P.,  AND RICHARD ?. WlNrlELO.   1934,   USER'S  GUID=  FOR  WASTOX,
A FRAMEWORK  FOR  MODELING THE FATE 0= TOXIC CHEMICALS  IN  AQUATIC  ENVIRONMENTS,
PART l:  EXPOSURE  CONCENTRATION.  EPA-600/3-84-077,  U.S.  ENVIRONMENTAL
PROTECTION   AGENCY,   ENVIRONMENTAL  RESEARCH  LABORATORY,   GULF   BREEZE,   FL.

   A  COMPUTES   P:?O;RAM  WAS DEVELOPED FOR MODELING   TH=  ^TE   OF   TOXIC
   CHEMICALS  THAT  ARE DISCHARGED TO NATURAL  tfATER  SYSTEMS.   THE   PROGRAM
   PERMITS   THE   USER  TO MODEL THE WATER AMD   SEDIMENT   TRANSPORT   IN  A
   NATURAL  WATER SYSTEM AND THE MOVEMENT AND  DECAY  OF  CHEMICALS
   DISCHARGED   TO   THAT SYSTEM. EITHER THE  EQUILIBRIUM   DISTRIBUTION   OF
   CHEMICALS  CONTINUALLY DISCHARGED TO THE SYSTEM  DR  THE   CONCENTRATIONS
   IN THE SYSTEM AS A FUNCTION OF TIMS MAY 3E COMPUTED,  FROM  ONE  TO  THREE
   TYPES  0= SOLIDS MAY 86 CONSIDERED. THE REACTION  OP THE  CHEMICAL  AND
   ITS TRANSFER  AMONG PHASES ARE COMPUTED FROM  SPECIFIED  CHARACTERISTICS
   OF  THE   CHEMICAL  AND ENVIRONMENTAL PARAMETERS   OF  THE   SYSTEM.  THE
   PROCESSES  CONSIDERED INCLUDE PHOTOLYSIS,  HYDROLYSIS,  BIODEGRADATION,
   VOLATILIZATION AND ADSORPTION. ADSORPTION  TO  THE  SOLIDS  TYPES  INCLUDED
   IN THE MDOEL  IS DESCRIBED AS A LOCAL EQUILIBRIUM  PROCESS DEFINED  BY  A
   PARTITION  COEFFICIENT AND THE LOCAL SOLIDS  CONCENTRATION.  ALL   OTHER
   PROCESSES  ARE  DEFINED IN TERMS 0*= REACTION  RATES.  VIASTOX   DOES  NOT
   EXPLICITLY  SPfcCIFY EACH OF THE TRANSPORT PROCESSES  THAT  MAY AFFECT  THE
   CHEMICAL  ?R   SOLIDS. TRANSPORT IS CONSIDERED EITHER  AS  AN   ADVECTIVE
   PRDCESi  DEFINED 3Y A FLCW OR A MIXING PROCESS DEFINED  BY A  DISPERSION
   OR  EXCHANGE.  SPECIFICATION C? SEPARATE TRANSPORT  PROCESSES IS  MADE   3Y
   THE USER BY DEFINING UP TO NINE SETS OF FLOWS AND  DISPERSIONS   CTERMED
   FIELDS),  EACH  -I?L-D  IS  APPLIED TO  EITHER  DISSOLVED   CHEMICAL   OR
    ADSORBED CHEMICAL  AND SOLIDS, 3R BOTH. FOR EXAMPLE, DISPERSION  WITHIN
   THE  STATIONARY ScDIM-NT IS LIMIT-ED TO DISSTLVED  CHEMICAL;  THEREFORE  A
   FIELD  0= DISPERSIONS WOULD 8E SPECIFIED 8Y  THE  USER  AND APPLIED   ONLY
   TQ  THIS  COMPONENT. THE USE OF SUCH A NON-SPECIFIC  TRANSPORT   STRUCTURE
    PERMITS   CONSTRUCTION OF MODELS CONSISTENT WITH  THE  UNDERSTANDING   OF
   THE  PARTICULAR NATURAL WATER SYSTEM AND THE  QUESTION  BEING  ADDRESSED.
   ^ASTDX   IS  SUFFICIENTLY GENERAL TO BE APPLIED TO  ALL  TYPES OF   NATURAL
    WATER   SYSTEMS.  IT HAS BEEN SUCCESSFULLY  APPLIED  TO  THE   JAMES   RIVER
   ESTUARY, THE GREAT LAKES, AND THE U.S. ENVIRONMENTAL  PROTECTION  AGENCY
    CEPA)  EXPERIMENTAL STREAM CHANNELS AT MONTICtLLO,  MINNESOTA.
                                   PAG:

-------
CONNOLLY,  JO-N   ?.,  MARY E, CLEVELAND,  AND  PARMP'Y «   PPTTCHARD   IN  PREP.
VALIDITY  OF  PARTITION COEFF         '
                                                                               .
                        COEFFICIENT A'  THE  AOSHRPTIPN  OFffTPTn   TM  =YPOSURE
                P» -niTTT TMC . cTin-r-r-  "      AJiJKPTiUN  OESCRIPTOR  IN  =XH05UKt
                PREDICTIONS STUOItS  WITH REPONE  AND M£THYL  PARATHION,  WATER
R c o •   v c K L » o r 4 1 5 / •
                        ^ I-RS« MJOR ^SUMPTIONS  IMPLICIT IN THE USE  OF
                              SOLE AOSOR"ION  DESCRIPTOR:   CD  ADSORPTION
                          ANT TO FATE AND  TRANSPORT  OF  THE  TOXIC  CHEMICAL
                T             <2) A3S3*PTIOM  IS  A  REVERSI3L;  PROCESS;  AND
                IUM  CONDITIONS A:?E INDEPENDENT  Of TH =  INOIVTQUAL
   nTHn?5   ?n-n^nCHE''ICAL ANO  "SDRBINti  SOLID,  DEPENDING  ONLY
   ON THEIR hATIt,.  ADSORPTION Of KEPONE AND METHYL  PARATHION WAS FOUND TO
   BE  RAPID   AMD  T*Q-ST£P, A FAST  ADSORPTION  FOR   APPROXIMATELY  5  MIN.
   FOLLOWED BY A  SLOWER ADSORPTION  TO EQUILIBRIUM  AT  1  TO  2  HR.  KINETICS
   OF , ADSORPTION   INDICATED  ADSORPTION  RATE   WAS   CONTROLLED  3Y  MASS
   TRANSPORT   MECHANISMS.  KINETICS OF METHYL  PARATHION  ADSORPTION  WERE
   IDENTICAL  =OR  STcRIL: AND BIOLOGICALLY ACTIVE SYSTEMS  TO  THE POINT  OF
   STcRILE  SYSTEM  EQUILIBRIUM. CONTINUED DECREASE  OF  DISSOLVED  14C  AND
   TOTAL  MASS RECOVERY IN THE ACTIVE SYSTEM  SUGGESTED  DEGRADATION TO  AN
   IRREVERSIBLY -DSOR3ED COMPOUND.  THE RESULTS  INDICATE THAT KINETICS CAN
   5t IGKaS-D  C1R  SMALL PARTICLE SIZE SEDIMENTS  BUT THAT  REVERSIBILITY OF
   ADSORPTION  CAN'JQT 3E ASSUMED, EQUILIBRIUM  ADSORPTION OP BOTH COMPOUNDS
   AT CONSTANT StQIMENT CONC£"iT^ ATION WAS DESCRIBED BY  A  LINEAR ISOTHERM.
   PARTITION   COEFFICIENT WAS, HOWEVER, AN  INVERSE  FUNCTION   OF  SEDIMENT
   CQNCcNTRATIO.N,  DECREASING BY AS  MUCH AS  AN  ORDER OF  MAGNITUDE  BETWEEN
   SEDIMENT   CONCENTRATIONS  REPRESENTATIVE   OF  SUSPENDED  SEDIMENT  AND
   SEDIMENT   CONCENTRATIONS REPRESENTAIVE OF  3ED SEDIMENT.  THEREFORE,  A
   SINGLE PARTITION COEFFICIENT IS  INADEQUATE  FOR  EXPOSURE  CONCENTRATION
   PREDICTIONS.

CONNOLLY, JOHM P.,  AND »06ERT V. THOMANN.   IN  PRESS.  HASTOX, A FRAMEWORK  FOR
MODELING  THE  FATE  OF TOXIC CHEMICALS IN  HQUATIC ENVIRONMENTS, PART  21  FOOD
CHAIN.  EPA/600/4-85/040, U.S. ENVIRONMENTAL  PROTECTION AGENCY, ENVIRONMENTAL
RESEARCH LA309AT03Y, GULF BREEZE, FL.  52P.

   A  FOOD CHAIM  31 04 CCUMULATIOM MATHEMATICAL  FRAMEWORK WAS  DEVELOPED  AS
   PA3T  OF A  BROADER FRA'-IEWCRK FOR M-JDELING  THE FATE  0=  TOXIC  CHEMICALS
   IM  NATURAL WATER SYSTEMS, ENTITLED WASTOX.  A USER'S GUIDE FOR  WASTOX
   CEPA-600/3-84-077)  WAS  PUBLISHED  IN AUGUST   1984.  THE  FOOD  CHAIN
   COMPQNCNT   OF   WASTRX  DESCRIBED  HERE   IS   A   GENERALIZED  MODEL  FOR
   ESTIMATING   THE  UPTAKE AND ELIMINATION 0s2  TOXIC  CHEMICALS  BY  AQUATIC
   ORGANISMS.  UPTAKE AND ELIMINATION RATES  ARE  RELATED  TO  THE
   BIOENcSG^TTC PAPAM-T-RS OF THE SPFCIES ENCOMPASSED  IN  EITHER A  LINEAR
   FOOD C^iAIN^O?  5  FOOD WS6. CONCENTRATIONS ARE  CALCULATED AS A  FUNCTION
   OF  TIMF   AND   AG= FOR EACH SPECIES INCLUDED. EXPOSURE   TO  THE  TOXIC
   CH^MIC^L   IN  =OOD IS BASED ON A CONSUMPTION  RATE   AND  PREDATOR-PREY
   RELATIONSHIPS  THAT ARE SPECIFIED AS A  FUNCTION  OF  AGE.  EXPOSURE TO THE
   TOXIC  CHEMICAL   1*1 WATER IS FUNCTIONALLY  RELATED  TO  THE  RESPIRATION
   9ATE   STEADY-STATE CONCENTRATIONS MAY ALSO  BE  CALCULATED. FOOD  CHAIN
   EXPOSURE TO CHEMICALS '^AY 3E SPECIFIED BY  THE USER  OF  THE MODEL OR MAY
   BE TAKFN DIR=CTLY ^ROM THE VALUES CALCULATED  3Y  THE  EXPOSURE
   CONCCNTRATIO'1   COMPONENT  OF  WASTOX.  MIGRATORY  SPECIES,   JS  WELL  AS
   NO'HIG!>ATORY S^CIFS, MAY 8£ CONSIDERED. THE  MODEL  HAS  BcEN
   sScCESSFULL? 5sEO TOMarEL KEPONE IN THE J^MES  RIVER STRIPED BASS FOOD
   CHAIM  AND   PCSS IM THE LAKE MICHIGAN  LAKE  TROUT FOOD   CHAIN  AND  THE
   SASINAW BAY, LAK.-E HURON YELLOW PERCH F'THD  CH^IN.
                                  PAGE   16

-------

              FAT'   F  TOX r 'r
                J'.rSM?
               ,  HT  ,  o-;~
               MENTAL  RrSZA
                                LABORATORY,
                                                            X,  A  FRAMEWORK  FOR
                                                  ENVIRONMENTS.  'ART  2:   FOOD
                                               U.S.   ENVIRONMENTAL   PROTECTION
                                                 BREEZE,  FL.   8P.
COOK, W.L., D6NISE  FIEDLE
  n
AND
AVAIL, FR3M
            NTISt
                           ,  AMD A.W. 30URQUIN.  1980.  SUCCESSION
                          HICROC-1S'-'S PERTURBS SY CARBARYU  METHr
                         B3T, MAR,  23(2) : 129-131.  CERL.G3 397*).
                   SPRINGFIELD,  VA :  P381-129512.
                                                                      PARATHION
   THE EFFECTS
   HICR3FUNGAL
                OF  CAR3ARYL, METHYLPARATHION AMD  PENTACHLOROPHENOL  ON  THE
                 S:)CCESSIOM  OF  AM  ESTUARINE  MICROCOSM   WERE   EXAMINED.
   RESIDENT   FUNGI  WrRE SUCCEEDED BY FUSARIU'1   IN  THE   CARBAR YL-TREATED
   MICRJCOSM;   3Y  A FJNGUS IN THE PENICILLIUM CHRYSOGENUM  SERIES  IN  THE
   METHYL PAfUTHiaN-TREATED MICROCOSM; AND 3Y A  FUNGUS IN  THE PENICILLIUM
   CANESCENS   SERIES  IN THE PEMTACHLOROPHENQL TREATED  MICROCOSM.   SMALL
   QUANTITIES   OF   14C02 WERE RELEASED FROM THE  XENQBIOTIC   MOLECULES   3Y
   FUNGI S5L5CTEC  CRC'^ TH£ MICROCOSMS.
CRIPE,  C.R.  1980.   APPARATUS TO PRODUCE TIDAL FLUCTUATIONS IN  A
SALT MARSH SYSTEM.   PROG.  FISH-CULT.  42Cl):32-33.  (ERL.GB X050).
                                                                      SIMULATED
   THE AP-'AKATUS  3ESC
   PESTICIT: DYNAMICS
   LIVINGSTON   1977)
   DEEP.  VUTER ENTER
   ANO  HHAD63X   ARRA
   EXCU3RENT  SIPHON
   3EAR ASSEMBLY  (FIG
   LATEX TUBING,  HAD
   TANK F10M SIPHONIN
                      RI?EO HERE (FIG, 1)  WAS DESIGNED TO  AID  IN   STUDYING
                       IM SIMULATED SALT MARSH SYSTEMS (CRIPE  AND
                       AND USED CIRCULAR TANKS 3 M  IN DIAMETER  AND  0.6   M
                      ED THE TANKS CONTINUOUSLY AT  3 L/M THROUGH A  SIPHON
                      NGEMENT  A'^JO  DISCHARGED  THROUGH  A   CONSTANT-LEVEL
                      CFIG. 2) THAT WAS RAISED AND  LOWERED  BY  A MOTOR   AND
                      .  3). THE EXCURRENT  SIPHON, MADE OF  2.5-CM GLASS  AND
                      4  SM3LL AIR TUBE AT  ONE OF THE BENDS  TO  PREVENT   THE
                      G  3ELQW THE LEVEL OF THAT SEND.
    £,  C.R.   1979.  AUTOMATED  DEVICE   (AGARS)   FDR  _STUDYING   AVOIDANCE   OF
POLLUTANT  GRADIENTS 3Y AQUATIC ORGANISMS.   J. FISH. R=S.  BOARD  CAN.
36(15:11-16.  (E
AVAIL. FROM
             NTTS,
                   ,GB  X051*).
                   S°RINGFI£LD,
                                VA;  PS-29^  363
   MOST  AP
   ORGANISM
   POLLUTAN
   SYSTEM)
   ALLOTS
   INCREASI
   EXTENDED
   MicR'jpRO
   TA^-  RF
   ANIMALS"
   TEST EXP
   RHCM3CIO
   OXIDANTS
            PARATUS DESIGNED TO DETECT  AVOIDANCE  OF  POLLUTANTS  BY   AQUATIC
            S   REQUIRE  VISUAL  JBSERV ATICNS  OP TEST   ORGANISMS  IN  STEEP
            T  GRADIENTS. AGARS (AQUATIC  GRADIENT  AVOIDANCE  RESPONSE
            WAS   DEVELOPED TO ELIMINATE  THESE  LIMITATIONS.  THIS   SYSTEM
            ANIMALS  T3 CHOOSE BETWEEN  ONE  UNC1NTA MINATEO ZONE   AND  THREE
            NGLY   TOXIC ZONES IN A GRADIENT TROUGH THAT  IS   MONITORED  FOR
              TIME  PERIODS  BY  INFARSD  LIGHT  SOURCES,  SENSORS,   AND  A
            ^FSSOR.  DATA ARE ACCUMULATED HOURLY  AND  PROCESSED  BY  A  PAPER
            ADER/CALCULATOa/PLOTTE*   SYSTEM  THAT RECORDS   THE   TIME  TEST
            R^«AIM IN E^CH ZONE AND  COMPARES BEHAVIOR BEFORE   AND   DURING
            OSURES. INITIAL TESTS INDICATE  THAT =>INFISH  (LAGODQN
            =S)   TESTED  IN  THE APPARATUS  ^ILL   AVOID  CHLORINE-PRODUCED
            AT  CO'-iC-NTRATIONS 0? 0.02-0.04 MG/L.
                                   PAGE   17

-------
C.R., AND  3.E.  STOKES.  1978.  DEVICE
                                              Tr
                                                      DANGEROUS
   THE   USE  OF
   SALTWATER  H
   BREAKING  OF
   HEATER CUE T
   CONTACT  WIT
   COSTING LESS
   DIFFERENTIAL
   ACTIVATE  AN
   RELAY. THE V
   RESET 3UTTON
i, tSr? I 120~V  ALTERNATING  CURRENT  IM   A  LABORATORY  WITH
3L3ING TANKS  PRESENTS  A  POSSIBLE  HAZARD TO PERSONNEL.  THE
 A GLASS-ENCLOSED  MATES  HEATER  OR MALFUNCTION OF  A  METAL
0 CORROSION COULD  RESULT IN A  LETHAL SHOCK TO A PERSON  IN
H  THE WAT.= P  AND  A  GRDUNO.  THE  APPARATUS  DESCRIBED  HERE,
 THAN 140 (JANUARY  1977),  IS  DESIGNED  TO DETECT A  VOLTAGE
  BETWEEN A CONTAINER  OF S^LT  WATER AND A GROUND. IT  WILL
  4LAR*1t  AND TURN  OFF THE  CURRENT  TO   A  HEATING  ELEMENT
OLTAGE WILL REMAIN  OFF AND  THE  ALARM WILL CONTINUE UNTIL A
 IS PRESSED.
CRIPE, C.R., AND  R.J.  LIVINGSTON.  1977.  DYNAMICS
PHOTOPR3DUCTS   IN A  SIMULATED MARSH SYSTEM.  ARCH.
5(35:295-303.   (ERL.G3 X048).
                                     OF MIREX
                                     ENVIRON.
                                                       AMD  ITS
                                                       CONTAM.
PRINCIPAL
 TOXICOL.
   THREE  SIMUL^Tru  MARSH SYSTEMS WERE CONSTRUCTED, CONTAINING  SEDIMENT,
   MARSH  PLANTS,  OYSTERS, 3LUE CRABS, CIDDLES CRABS, AND TWO SPECIES   OF
   TOP  MINNOWS.  SEAWAT5R ENTERED EACH OF THE POOLS BY FLOWING  ACROSS   A
   TROUGH,  TWO   3F  WlICH C3NTAINED MIREX BAIT. TIDAL  FLUCTUATIONS  WERE
   SIMULATED.   SAMPLES  OF  WATER, BAIT, AND  ANIMALS  WERE  PERIODICALLY
   ANALYZED.  -ALL  aNIWALS CONCENTRATED MIREX, THREE PHOTQPROOUCTS
   ACCUMULATED  ON  THE BAIT PARTICLES, AND BOTH 3YSTERS AND ONE SPECIES  OF
   FISH ACCUMULATED  QN£ OF THE PHOTOPRODUCTS.

CROW,  S.A.,  D.G.  AHEARN, W.L. COOK, AND A.W, BOUSQUI'I.  1975,  DENSITIES   OF
BACTERIA AND  FUNGI IN COASTAL SURFACE FILMS AS DETERMINED BY A
MEMBRANE-ADSORPTION  PROCEDURE.  LIMMOL. OCEANOGR.  20C4):644-646.  (ERL,GB
232).

   A  MEMBRANE-ABSORPTION TECHNIQUE FOR COUNTING SURFACE SLICK  MICROBIAL
   POPULATIONS   WAS   EVALUATED. THE SIMPLE  PROCEDURE  GAVE  BACTERIAL   AND
   FUNGAL   POPULATIONS  SEVERAL ORDERS OF MAGNITUDE   GREATER  THAN  THOSE
   PREVIOUSLY REPORTED F0« SU3PACE SLICKS.
CkOW,  S.A.,   P.I.   BOWMAN, AND D.G
CANDIDA ALB 1C INS  FROM THE NORTH SEA,
33C3):738-739.   (£RL,GE X052*).
                        AHEARN,  1977,
                        APPL. ENVIRON,
                                                 ISOLATION
                                                MICROBIOL.
                                                                   OF   ATYPICAL
   ISCLAT^S   ''IF   CAMOIDA  ALBIC4NS  '--'ITH   SPARSE   FILAMENTATION   AND   WEAK
   FERMENTATION   HP$C ISOLATED -RDM THE  SURFACE  HICRCLAYER  DF   THE   NORTH
   SEA,   ?UT   NIT FRCM SUBSURFACE WATERS.  SUCH  ATYPICflL  ISOLATES  MAY  BE
   MISIOEMTIFIEO  3Y USING NORMAL TAXONOMIC  PROCEDURES,
                                  PAGF   18

-------
                         ,,                     ..           .   1976.  MICR03IAL
                        !>URF4Cfc  SLICKS.   IN:   PROCEEDINGS  OF  THE THIRD
INTERNATIONAL   ilDOEGRADATIOK   SYMPOSIUM.   J.M.   SHARPLY  AND  A.M.  KAPLAN,
EDITORS, APPLIED  SCIEMCE PUBLISHERS, LTD.,  LONDON.   PP/93-98.  (ERL,G8 254).

   SAMPLES  OF  TIE   UPPER 10 MM  3F  INSHORE  SURFACE  FILMS   OBTAINED  8Y
   ADSORPTION TO  MEMBRANES YIcLDEO MICRQBIAL  POPULATIONS  UP  TO 10 TO  THE
   clbHT  POWcR   ML-1 OR 10 TO  THE FIFTH  POWER  CM -2.   THESE  POPULATIONS
   WE'^E TYPICALLY 10-100 TTME3  GREATER  THAN THOSE IM UNDERLYING WATERS AT
   A  DEPTH 0 =  10 CM. PREDOMINANT BACTERIA  IN SJR=ACE  FILMS  WER*  MOTILE,
   N'JNPIG.'IENTED,   GfiAil-NEGATIVE RODS. CCLQNY-FOSMING UNITS OF Y=ASTS  AND
   MOULDS WER.S  -OOND IN CONCE\'TSATION3  TO 10  TO  THE  FOURTH POWER ML-1  OR
   28 CM-2. THE  PREDOMINANT SPECIfS  IN  SURFACE  FILMS WERE PRCTEOLYTIC AND
   AMYLCLYTIC   5UT cXHISITED  DfiLY WEAK  TO NEGLIGIBLE  HYDROCARBONOCLASTIC
   AND  L1POLYTIC  ACTIVITIES.  A  GREATER PROPORTION  OF THE  SURFACE  FILM
   BACTERIA,  AS CDMPAi?ED TO THOSE AT 10 CM  OE°TH, WERE CAPABLE OF  GROWTH
   ON FRESH-WATER W5CIA,

 CROW,   S.A.,   S.L,  BELL,  AND D.G.   AHEARJJ.  1980.   UPTAKE  OF  AROMATIC  AND
 o^ANCHEJ  CHAIN  HYDRQCARdOMS BY  YEAST. BQT.   MAR.  23C3):117-120.  CERL,GB
 X183*).
 AVAIL.  FROM  NTIS, SPRINGFIELD,  VA:   P881-126567.

    STUDIES   Oc    THE HYDROCARBON UTILIZING YEASTS CANDIDA  MALTOSA  AND  C.
    LIPOLYTICA  ^AVe S'-IU^M  THAT  BOTH  WERE CAPABLE OF  REDUCING  RECOVERABLE
    AMOUNTS   0^  BRANCHED  CHAIN AND AROMATIC  HYDROCARBONS IN A  MIXTURE  OF
    NAPHTHALENE,  TETRAOECANE,  HEXADECANE, PRISTANE
    CTETRA-M:THYLPSNTAOECA?JE).  CELLS  OF C. LIPOLYTICA  GROWN  ON  EITHER
    GLUCOSE  OR TET'ADECA'JE  WERE  CAPABLE  OF BINDING (RENDERING
    UNEXTRACTASLS)  NEARLY  50% OF  THE HYDROCARBON MIXTURE  WITHIN 3  HOURS.
    IN   CONTRAST  CELLS 0?  C.  MALTOSA  BOUND HYDROCARBONS ONLY AFTER  GROWTH
    DM  A HYDROCARBON MEDIUM.  UPT&KE  OF SELECTED PARAFFINIC HYDROCARBON WAS
    NOT   ALTERID   ; Y  THE  PRESENCE OF  NAPHTHALENE.   P3TSTANE  UPTAKE  WAS
    CONCENTRATION  DEPENDENT   FOR  C.  MALTOSA B'JT NOT   FOR   C.  LIPOLYTICA.
    UPTAKE,  TRiNSPJRT, AND  METABOLISM ;3F HYDROCAR6JNS IN C. MALTOSA AND C.
    LIPOLYTICA OfF'ER.
                                   PAGE  19

-------
                   alrr^'f "*  l9"*  FATTY ACID CHARACTERIZATIONS  OF   SELECTED
                   BACTERIA AND SEDIMENTARY COMMUNITIES.   PH.D.   DISSERTATION.
FLORIDA STATE UNIVERSITY, TALLAHASSEE, FL.  132P.   (E.
         rH  WAS USED TD CLARIFY THE TAXONOMY   ^   SULFATE-REOUCING
   BACTtKlA   (SRB)   T3  DETERMINE  THE  COMPOSITION   OF   SULF 4T=-REDUCING
   COMMUNITIES.  THE PHOSPHQLIPID FATTY ACID COMPOSITION  OF   OESULFOVI8RIO
   DESULFURICftNS,  C ESULFOTOMACULUM QRJENTIS, OESULFQTOMACULUM
   NIGRIFICANS,   AND  FJUR  SRB ISOLATED FROM  SALT  M4R3H   SEDIMENT   WERE
   DETERMINED BY CAPILLARY GAS-LI JUID CHRDMATDGRft PH Y  AND  MASS
   FRAGMENTOGRAPHY. THE FATTY ACID COMPOSITIONS OF THE SRB  WERE   COMPARED
   USING MULTIVARITc STATISTICS AND CONTRASTS" TO THE FATTY  ACID
   COMPOSITIONS   OF BACILLUS SUBTILUS, CLOSTRIDIUM BUTYRICUM,   PSHERICHIA
   COLI,  PStUDlMONAS PUTIDA, MHRAXELLA SD. AMD ATHR03ACTER  SP.   ALL   SRB
   EXAMINED   CQNTAI?JEn  PREDOMINANTLY  ISO AND  ANT5ISO   METHYL   BRANCHED
   ACIDS.   DESULFOVIR!?ia  DES'JL^USICANS,  D5SULFOTOMACULUM   ORI5NTIS   AND
   DESULF3TOMACULJM NIGRIFICANS CONTAINED HIGH PROPORTI3NS  OF  AN  UNCOMMON
   17  CARSON  ISO  MONOUNSATU8ATEO ACID. THE MAJOR DIFFERENCES   IN  FATTY
   ACID COMPOSITIONS AMONG SRB WeRE QUANTITATIVE WHILE THE  MAJOR
   DEFERENCES 3tTWcEN SR3 AND THE OTHER SACT5RIA EXAMINED  WERE
   QUALITATIVE,  THE FATTY ACID COMPOSITION OF  BACILLUS SU3TILUS  WAS   MOST
   SIMILAR   TO THOS: OF THE SR8 IN THflT IT CONTAINED  HIGH PROPORTIONS  OF
   BRANCHED   SATURATED  AND M3NOUNSATURAT5D ACIDS.  ESHERICHIA   COLI   AND
   CLDSTRIDIU^'1 3UTY3ICUM WERE CHARACTERIZED 8Y HIGH PROPORTIONS  OF  16 AND
   18  CARBON  SATURATED  STRAIGHT CHAINED ACIOS AND  17  AND   19  CARBON
   CYCL3P30PAME   ^CIDS.  PSEUDC^ONAS  PUTIDA AND MORAXSLLA   SP.   CONTAINED
   HIGH PROPORTIONS OF 16 AND 13 CARBON MONOUNSATURATcD  ACIDS.  THE  FATTY
   ACID  COMPOSITION OF ARTHR3BACTER  SP. WAS QUITS SIMPLE IN THAT 90%  OF
   THE 4CICS WAS AN ISO METHYL BRANCHED 15 CARBON ACID.  THF   PHOSPHOLIPID
   FATTY ACID COMPOSITION OF THE MICRQBIAL COMMUNITIES OF FRESHWATER   AND
   £STUARI*iE SEDIMENTS WERE DETERMINED 3Y ANALOGOUS METHODS. THE
   FRESHWATER SEDIMENTS WERE CHARACTERIZED 3Y  PHOSPHOLIPID  CONCENTRATIONS
   100  TIMES HIGHER THAN ESTUA^I'^E SEDIMENTS  AND BY  HIGH PROPORTIONS  OF
   STRAIGHT-CHAINED  SATURATED ACIDS. HE ESTUA8INE   SEDIMENTS   CONTAINED
   HIGHER   PROP1RTIONS 'IF BRftNCHED AND MONOUNSA TURATED ACIDS.   THE  LIPID
   CONTENT   Op ALL SEDIMENTS GENERALLY DECREASED WITH DEPTH AND   ISO   AND
   ANTEIS*  BRANCHED ACIDS BECAME MORE ABUNDANT. ESTUARINE SEDIMENTS TAKEN
   FROM  THRE- LOCATIONS ALHN3 A 10 METER TRANSECT THROUGH  A  SALT  MARSH
   WFRE  SHOWN TO VARY 10 FOLD IN  LIPID CONTENT AND BY A  FACTOR   1000  IN
   RATES   0= 3ULFATE RESPIRATIONS. DIFFERENCES IN  HICROBIAL  COMMUNITIES
   WERE DEMONSTRATED 3Y THEIR PHOSPHOLIPIO FATTY ACID COMPOSITIONS  AND BY
   THEIR METABOLISM 0= CARBQN-14 LABELED  SUBSTRATES..
                                   PAGE  20

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GARNAS, R.L.t A.W.  3DURQUIN, AMD P.M. PRTTCrlARD,  1978.  ^ATE AND  DFGRAOATION
OF  14C-KEPONE   IN   ESTUARINE  MICROCOSMS.  IN:  PROCEEDINGS  OP   THE   KEPONE
SEMINAR  II.  EPA-9Q3/9-73-C11, U.S. ENVIRONMENTAL PR3T-CTION AGENCY,   REGION
III, PHILADELPHIA,  PA.   PP. 330-352.  CtRL.SB 351*).

   THE  FATE  0^   14C-KcPON= WSS STUDIED IN STATIC  AND  CONTINUOUS  -LOW
   ESTUARINE  MICR1CQSMS. 3IOTIC AND ABIOTIC TRANSFORMATION AND
   VOLATILIZATION;   WERE NOT IMPORTANT PROCESSES IN THESE STUDIES.  KEPONE
   DESQRBED READILY FROM SALT MARSH SEDIMENTS AND JAMES RIVER  SEDIMENTS.
   WHILE  THIS  DESORPTION WAS INDEPENDENT OF  ENVIRONMENTAL  TEMPERATURES
   AND SALINITY RAN3FS, KEPONE RESIDUES IN SEDIMENT INFLUENCED
   CONCENTRATIONS  IM WATER COLUMN. RADIOACTIVITY WAS NOT EXTRACTA8LE FROM
   SOME JAMES RIVER SEDIMENTS, USING ?£COGNIZ-D ANALYTICAL PROCEDURES.  IN
   LARGER CONTINUOUS FLOW SYSTEMS, 3E-JTHIC POLYCHAETES (ARENICOLA
   CRISTATA)  ACCUMULATED HIGH RESIDUES OF KEPONE, DIED, AND  DECOMPOSED.
   THESE  RESIDUES   WERE  NEVER  AVAILABLE  FOR  DESORPTIQN  COMPARED   TO
   SEDIMENT.  THESE  DATA  WILL ALLOW BETTER PREDICTION OF  THE  FATE   OF
   KEPONE IN  THE  4'wUATIC ENVIRONMENT.

HOLZSCHU, D.L., F.W. CHANDLER, L. AJELL3, AND D.G, AHEARN.  1979.  EVALUATION
OF INDUSTRIAL YEASTS =OR  PATHOGENICITY.  SABOURAUDIA.  17(1):71-78.  CERL.GB
X088*).

    ELEVEN   YEASTS  REPRESENTATIVE OF SPECIcS Dc INDUSTRIAL  INTEREST  WERE
    COMPARED   WITH  CANDIDA ALPICANS FOR THEIR POTENTIAL PATHOGENICITY  FOR
    UNTREATED  AND  CORTISONE-TREATED MICE. ONLY C. TROPICALIS  PRODUCED   A
    PROGRESSIVE  INFECTION SIMILAR TO THAT PRODUCED BY C. ALBICANS.  CANDIDA
    LIPOLYTICA,  TORULODSIS SPP., AND HANSENULA POLYMDRPHA WERE NOT
    RECOVERED  FROM  MICE 6 OAYS AFTER INOCULATION. KLUYVEROMYCES  FRAGILIS,
   C.  PSEJDOTRO°ICALIS, C. UTILIS, C. GUILLIERMONDII AND C. MALTOSA  WERE
    RECOVERED  F1QM  MICE  BUT  DID NOT  PRODUCE  EVIDENCE  OF  INFECTION.
                                  PAGE   21

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KUCKA, G.H., AND  D.T. GIBSON.  1981.   SACT^AL  DEGRADATION OF
™£™^                                                             u-s-
BRE£Zt! F 1   74P            -GcNCY,  ENVIRONMENTAL   RESEARCH  LABORATORY,  GULF
     ---r-^: ^S;1:3- 9*16'  STRAI*  "•  ^SN  GROWN ON SALICYLIC  IN
   THc PRcScNCt  0^ DI3ENZO-P-OI3XIN,  ACCUMULATED
   CIS-1,2-OIHY9R3XY-1,2-OIHYQRODIBENZO-P-DIQXIN  AND
   2-HYDROXYDIBENZO-P-DIOXIN   IN  THE  CULTURE  MEDIUM.  CRUDE CELL  EXTRACTS
   PRcPAREu   rR-lM  THE PARENTAL STRAIN  GROWN   WITH  NAPHTHALENE  OXIDIZED
   CI5-1,2-DIXHYDRCXY-1,2-DIHYD^QOIBE'MZO-P-DIDXIN  TO
   1,2-DiHYDROxYDiBENza-p-DioxiN. FURTHER   DEGRADATION OF  THE  METABOLITE
   WAS   N3T  DETECTED. WHOLE CELLS  OF  THE  PARENT STRAIN  0«=  B SI JERINCKI A ,
   GROWN   WITH  S'JCCINATE  AND 3IPHENYL,   OXIOIZED  DI35NZO-P-DIOXIN  AND
   SEVERAL  CHLQRINaTED DIOXIMS.  \ MUTANT STRAIN  C88/36) OF  3EIJERINCKIA
   OXIDIZED  DIB5NZO-P-DIOXIN  TO CIS-1 , 2-DIHYDROXY-l , 2-DIHYDRODI3ENZO-P-DIO
   XI.M.  T-^E  M'JTANT ORGANISM ALSO  OXIDIZED TWO MQNOCHLORINATED
   DI8EMZ3-P-OIOXINS  TO CI S-DIHYORODIOLS.  NO METABOLITES  WERE  DETECTED
   FROM  T.-IO  CICHLQRINATrD  DIPENZO-P-DIOXINS.  GROWTH  OF THC. PARENT  STRAIN
   OF  BEIJERINCKIA ON SUCCIMATE wftS INHIBITED AFTcR  FDUR HOURS WHEN 0.05%
   OlbENZG-P-DIOXIN  WAS   PRESENT   IN THE CULTURE   MEDIUM.  RESTING  CELL
   SUSPENSIONS  OF  THE PARENT ORGANISM OXIDIZED   DIBENZO-P-DIOXIN  TO  A
   CQMPOUMO  IDENTIFIED AS  1 » 2-DIHYDSQXYDI3ENZO-P-DIQXIN. FURTHER
   DEGRADATION  Oc THIS METABOLITE WAS  NOT  DETECTED,  AS THE COMPOUND  WAS
   FOUND  TQ  BE  A  °OTENT   MIXED-TYPE  INHIBITOR  Q^  TWO  RING-FISSION
   QXYGENASSS PRESENT I 'A THIS ORGANISM.

 KLECKA,  GSRY M., ANO DAVIO T. GIBSON.  1979.   METABOLISM OF DIBENZO
 C1»4)OIOXAN  BY A PS EUDO»-10NA S  SPECIES.  3IOCHEM.  J.   180C3) : 639-645 .  CERLtGB
 X091*).

   PSEUDQMONAS  SP. N,C,I,B.  9816  STRAIN  11*  WHEN  GROWN ON SALICYLATE  IN
   THE PRESENCE GF DI3ENZOC 1, ODIOX AN,  ACCUMULATED
   CI5-l,2-OlHYDROXY-l,2-DIHYDRaoiE:ENZO
-------
                           n-       N'   198°-  HSTABQLIS.M OF  DIBENZO-P-DIOXIN
        L      r M  »«   ,T  ,°XoNS 8Y A 3"J£"NCKiA SPECIES.  APPL.  ENVIRON.
       JL.   39C 2 ) : 2 88-296.  C£RL»GB X
   AND?HNY-T7~nnN °F "UERINCKIA, GROWN WITH SUCCINATE
   AND  oIPH.NYL, OXiOIZcD  DIBtNIO-P-DIOXIN AND SEVERAL CHLORINATED
   OIOXINS.  THc RATE  OF  OXIDATION OF Tri£  CHLORINATED  OIBENZO-P-DIOXINS
   DECREASED WITH AN INCREASING OEGREt OF CHLORINE SUBSTITUTION. A MUTANT
   STRAIN CB8/36) OF BEIJcRINCKIA OXIDIZED 01 3ENZD-P-OIOX IN TO
   CIS-1,2-DIHYDRGXY-1,2-DIHYORQDIB5NIO~P-DIOXIN. THE MUTANT ORGANISM
   ALSO  OXIDIZED  TW3 MONOCHLORIHATED OIBENZO-P-DI 3XINS .  GROWTH  OF  NO
   METABOLITES  WERE DETECTED FROM TWO  DICHLORINAT^D  DIBENZO-P-OIOXINS.
   GROWTH OF TH£ PAREMT STRAIM OF BEIJERIMCKIA ON SUCCINATE WAS INHIBITED
   AFTER  4  H  WHEM 3.05'i OI8ENZO-P-OIOXIN WAS PRESENT  IN  THE  CULTURE
   MEDIUM,  R«STHG CELL  SUSPENSIONS OF  THE PARENT ORGANISM,  PREVIOUSLY
   GROWN  WITH  SUCCINATE  AMD BTPH5NYL, OXIDIZED  DI8ENZO-P-DIOXIN  TO  A
   COMPOUND IDENTIFIEO ftS  1 , 2-DIH YDROXYDI8ENZO-P-OIOX IN. FURTHER
   DEGRADATION  OF THIS MZTABOLTTE WAS NOT DETECTED, AS THE COMPOUND  WAS
   FOUND TO EE  POTENT  MIXED-TYPE INHIBITOR OF TWO RING-FISSION OXYGENASES
   PRESENT IN THIS ORGANISE.

LAUGHLIN, ROGER A., CLAUDS R, CRIPE, AND ROfiERT J.  LIVINGSTON.  1978.  FIELD
AND  LABORATORY  AVOIDANCE REACTIONS 3Y BLUE CRABS CCALLINECTES  SAPIOUS)  TO
STORM  WATER -lU^C^F.   TSAMS.  AM. FISH.  SOC.  107C1) : 78-86.  CERL.G8  X180*).

   A  COMBINED  FIELD ANO  LABORATORY STUDY WAS CONDUCTED TO DETERMINE  THE
   AVOIDANCE  REACTIONS  OF  BLUE CRABS (CALLINECTES  SAPIDUS)  TO  HIGHLY
   COLORED, ACIDIC RUNOFF-  FROM CLEAR-CUT TIMBER AREAS ABOVE A  PRODUCTIVE
   NORTH  FLORIDA  ESTUARY.  SLUE CRABS OF TWO AGE  GROUPS  SHOWED  MARKED
   LABORATORY   AV3IDANCZ  OF  RUNOFF (PH 4.6, 5.8) ANO OF TEST  WATER  WITH
   EXPERIMENTALLY  REDUCED PH. WITHIN THE PH RANGE 4.5-7.0, THERE WAS  AN
   INVERSE RELATIONSHIP BETWEEN PH AND AVOIDANCE. WATER COLOR APPEARED TO
   PLAY  A  MINOR  ROLE  IN  THE  AVOIDANCE  REACTIONS.  FIELD  DATA  GAVE
   DIVERGENT RESULTS.  SMALL  CRA3S WERS ABUNDANT IN AREAS CHARACTERIZED BY
   PH  LEVELS STRONGLY AVOIDED UNDER LABORATORY CONDITIONS. LARGE  CRABS,
   HOWEVER,  WERE  CONSPICUOUSLY  ASSENT FROM SUCH AREAS  IN  THE  FIELD,
   INDICATING   POSSIBLE AVOIDANCE. FACTORS OTHER THAN PH WERE THOUGHT  TO
   BE  FUNCTIONAL  IN   THE FIELD DISTRIBUTION Or THE  CRABS.  THIS  STUDY
   INDICATES THAT LABORATORY EXPERIMENTS WITHOUT ASSOCIATED FIELD STUDIES
   MAY CAUSE MISLEADING RESULTS IF THEY ARE APPLIED TO A DETERMINATION OF
   IMPACT CRITERIA.

LAUGHLIN,  ROGER  A.,   CLAUDE  R. CRIPE,  AND  ROBERT  J.  LIVINGSTON.  1978.
REACTIONS  OF   BLUE  CRABS  TO  LOW  PH.  COMMENTS.  TRANS.  AM.  FISH.   SOC.
107(6^:863-371.  C£RL,G3 X047*),
                                  PAGE  23

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       IT '  1976    4in'n^rAUD= *' C'IPE* R03ER  A«  LAUGHLIN,   AND  FRANK  G.
        A.n  omp'MTM  -c-,NC£ RESPONS^ OF ESTUARINE  ORGANISMS TO STORM WATER
       /  ,M^^™tr   LUeNTS'  IN:  "TUARINE  PROCESSES,   VOL.  l:  USES,
       l'*r    lEf  nL   Sv T°oIH'Z ^STU^-  MARTIN  W.  WILEY,  EDITOR,  ACADEMIC
PRcSS, INL., NErf  YOrfK,  NY.  PP. 313-331.  CERL.GB  X049*>.
                                      T°  DETERMINE   THE   RELATIONSHIP  OF
   o,  ,,                   REACTIONS OF ESTUARINE  ORGANISMS   TO  SPECIFIC
   POLLUTANTS   AND  THEIR ACTUAL DISTRIBUTION  IN  THE   FIELD.   EXPERIMENTS
   HnJnPr JH?   ?EflCTIQNS ° F JUVENILE AND  ADULT BLUE   CRABS   CCALLINECTES
   nJ  ST ,LI   S!0in WATER RUNCFF AND LOW  PH,  AND THE  AVOIDANCE RESPONSES
   OF  PINFISH   CLAGOOON  RHOMBDIDES) TG 3LEACH6D  KRAFT   MILL  EFFLUENTS
   (BKMt).  THE  FIELD REACTIONS OF THESE  ORGANISMS  TO "(DINT   SOURCES  OF
   SUCH   POLLUTANTS  WERE MONITORED FOR RELATIVELY  LO?JG   PERIODS  IN  THE
   APALACHICOLA  ?iNO 4PALACHEE  3AY SYSTEMS  CN1RTH FLORIDA).  JUVENILE  AND
   ADULT  3LUE  CRA3S AVOIDED RUNOFF WATER FROM  CLEAR-CUT  FIELDS. THEY ALSO
   AVOIDED  WATER WITH EXPERIMENTALLY REDUCED  LEVELS  CF  PH SELOW 6.0.  IT
   HAS  FOUND   THAT THE LOW PH  OF THE STORM  WATER RUNOFF   WAS  A  PRIMARY
   FACTOR   IN   THE LABORATORY AVOIDANCE REACTION  OF  THE   CRABS.  HOWEVER,
   FIELD  STUDIES IN AREAS DIRECTLY AFFECTED  BY SUCH  RUNOFF INDICATED THAT
   ALTHOUGH   ADULT  6LUc  CRASS WERc USUALLY  NOT  FOUND   IN   SUCH  WATER,
   JUVENILE CRA3S ACTUALLY APPEARED IN HIGHER  NUMBERS  IN  PORTIONS OF  THE
   BAY  CHARACTERIZED  SY INCREASED RUNOFF  AND LOW  PH.  ALTHOUGH  PINFISH
   SHOWED   DISTINCT LA53RATORY  AVOIDANCE RESPONSES  TO  LOW LEVELS OF  3KME
   <0.1%, VOLUME/VOLUME), THEIR FIELD DISTRIBUTION  DID NOT  SUBSTANTIALLY
   CHANGE   AFTER  A POLLUTION A8ATEHENT PROGRAM WAS  INSTITUTED.  IN  THIS
   CASE,  IMC3MPLETE  TREATMENT  ANO/QR HABITAT   DESTRUCTION  COULD  HAVE
   ACCOUNTED   FOR SUCH BINDINGS, IN BOTH INSTANCES,  HOWEVER,   IT  APPEARS
   THAT   FACTORS 3THE3 THAN AVOIDANCE RESPONSE WERE  CONTRIBUTORY  TO  THE
   FIELD  DISTRIBUTION  OF THE  TEST SPECIES.  IT WAS  CONSIDERED  THAT  THE
   FIELD  RESPONSE OF ESTUARINE ORGANISMS  TO  VARIOUS FORMS  OF  POLLUTION
   WAS  T^  PRODUCT DF COMPLEX  PHYSICAL AMD  BIOLOGICAL FUNCTIONS SUCH  AS
   INTRASPECIFIC  AND  INTERSPECIFIC COMPETITION  AND  PREDATIQN,  HABITAT
   ALTERATION!   AND TROPHIC RESPONSE. IT APPEARS  THAT  LABORATORY  STUDIES
   WITHOUT  ASSOCIATED FIELD INFORMATION CAN  LEAD  TO SPURIOUS CONCLUSIONS.

 LLABRES,  CARLOS M., AND DONALD  G. AHEARN.   1985.  ANTIMICROBIAL ACTIVITIES OF
 N-CHL3RAMIN5S  A?JC DIAZOLIDIMYL  URSA.  APPL.  ENVIRON, MICROBIOL.
                 
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        I.E.T
           VOL  2
     »f <£RL J
                                 19?9'   CHARACTERISTICS 0- 3ACTERIA ADAPTED
                                 °NTARI°-   IN4   DEVELOPMENTS IN  INDUSTRIAL
                               °R INDUST«^ MICROBIOLOGY. WASHINGTON,   DC.
                                   IN ^UATIC ECOSYSTEMS DEPENDS, IN PART,
                          tS  °F  TH'E INDIGENOUS  MICROFLORA.  KNOWLEDGE   IS
                    OF  THt  GROWTH CHARACTERISTICS OF AQUATIC 3ACTERIA   IN
   LO-J  NUTRIENT CONDITIONS  TYPICAL OF MANY AQUATIC ENVIRONMENTS. WE  HAVE
   STUDIED  CHA^GcS   IN  3ACTERIAL POPULATIONS PROM  LAKE  ONTARIO  USING
   CONTINUOUS  CULTURE  ENRICHMENTS,  WITH LACTOSE AS THE SOL=  CARBON  AND
   ENERGY   SOURCE.  ENRICHMENT   STUDIES  HAVE SHOWN  THAT  THE  CONCN   OF
   LACTOSE,   THE  TYPE   OF  WATER UTILIZED FOR INFLOWING  MEDIA,  AND  THE
   INOCJLUM SOURCE AF^ECTtC  THE OUTCOME OF CONTINUOUS CULTURE ENRICHMENTS
   FROM FRESH-WATER SAMPLES.  TWO ISOLATES FROM ENRICHMENT EXPERIMENTS,  AN
   AERQMONAS  SP. AND A PSEUOOMQNAS  SP., WERE OBTAINED USING CONCN OF   50
   AND  5 MG/LITER LACTOSE,  RESPECTIVELY. THESE ISOLATES WERE SHOWN TO   3E
   COMPETITIVE WITH EACH OTHER  AT DIFFERENT LACTOSE CONCN. THE
   PSEUOOMONAS  SP. WAS MORE  SENSITIVE TO STARVATION AND  HEAT  TREATMENT
   THAN  THc AE30MOMAS  SP.  AND  DID MOT TAKE U? OXYGEN IN THE PRESENCE
   GLUCOSE  WHEN  CELL  SUSPENSIONS WERE PREPARED FRDM CULTURES
   PEPTONE 3RQTK,
                                                              GROWN
                                                                     OF
                                                                     IN
MAHAF=EY, W
ON  GROWTH
MICR03IOL.
         R.,
         AMD
             P.H.  PRITCHARO, AND A.W. 80URQUIN.  1982.  EFFECTS OF  KEPONE
             RESPIRATION OF SEVERAL  ESTUARINE  BACTERIA.  APPL.  ENVIRON.
             ):1^19-1424.  CERt,GB 367*).
TQXICITY  OF  K-5P3NE  TO MIXED POPULATIONS Or  ESTUARINE  MICROORGANISMS
iJAS DETERMINED  BY  STANDARD PLATE ASSAYS ON ZGBELL'S MARINE MEDIUM WITH
0.02,  0.20,  AND  2.0 MG K2P1NE PER LITER.  UNDER  AEROBIC  CONDITIONS
KEPONc  REDUCED   THE   NUMBER
CONCENTRATIONS   TESTED,   BUT I
MICROORGANISMS.  GRAM-POSITIVE
THAN GRAM-NEGATIVE  ORGANISMS.
INHIBITED IN COMPLEX  N-JTRIENT
A MINIMAL SALTS  8RQTH. CXYGEN
REDUCED  2Y  25-100%  BY  20 PPM
                               OF COLONY FORMING  UNITS  CCFU)  AT  ALL
                               T HAD NO EFFECT ON NUMBER  OF  ANAEROBIC
                               ORGANISMS WERE MORE SENSITIVE TO  KEPONE
                               GROWTH OF GRAM-NEGATIVE ISOLATES WAS NOT
                               BROTH? IT WAS SIGNIFICANTLY INHIBITED  IN
                               UPTAKE BY MOST PURE CULTURE ISOLATES WAS
                                KEPONE. OXYGEN EVOLUTION  WAS  OBSERVED
WHtN SEVERAL GRAM-POSITIVE ISOLATES WERE EXPOSED TO KEPONE
CONCENTRATIONS  OF  20  PPM. PENT ACHLOROPHENOL (PCP), HAD EFFECTS SIMILAR
TO  KEPONE   4T   COMCENTR ATIOMS  ABOVE 28  PPM.  KEPONE  INHIBITION   OF
=L£CTR3N  TRANSPORT  IS DEMONSTRATED BY A SIGNIFICANT REDUCTION IN  THE
SPECIFIC ACTIVITIES  OF NADH OXIDASSS AND SUCCINCOXIDASE.
                               PAGE  25

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MAHAFrEf, W.R.,  P.H.  PRITCHARO, AND A.w.  30URQUIN.   1979.   PH=NYLACETIC  ACID
METABOLISM  8Y   THREE  AQUATIC  3ACTE3IA  ISOLATED   FROM   CONTINUOUS  CULTURE
ENRICHMENTS.   IN:   DEVELOPMENTS IM INDUSTRIAL  MICROBIOLOGY,  VOL.  20.  SOCIETY
FOR  INDUSTRIAL   -1ICRGBIOLOGY, WASHINGTON, OC.   P<>.   489-495.   
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MUELLER, L.H.,  VI.  GILLUM, A.W. BQURQUIN,  AND  P  H   PRTTTHaPl   1Q34   FATE  OF
ePNTHTflM  TM   ? <\ 1 T  M ft r> r ._, r-.n.-.  -               f. n «  r K 1 1 On A K J •  lyo**-.  r -A I C  ur
                                                          *  «5LD  APPLICATION
                      RELEVANCE OF  LABORATORY  HATA CAN,  THEORETICALLY,  BE
              TK,   tlru  L      T"  °F  A  CH=*IC4L  IN THE  FIELD. THE  EFFORT
              ™  T^CH  *N ASSESSMENT  IS 0 = TEN  UNDERESTIMATED,  NOT  ONLY
            T£ T-J ITC.S   TIC*L  AN°   CLIMATIC  PROBLEMS  ASSOCIATED  WITH
            IN THE FIELD, BUT  BECAUSE  OF INSUFFICIENT INFORMATION
   NECESSARY   TO PROPERLY INTERPRET  FIELD  RESULTS. TH<=  COMMON USE OF  THE
   rn^TDnrH°^^n;T,INE-CTICIOE'  ^ENTHION,  IN SALT MARSH ENVIRONMENTS  TO
   CONTROL   MJS3UITO  POPULATIONS  GAVE  US  THE OPPORTUNITY TO  ASSESS  THE
   FATE Or  THIS  CHEMICAL UNDER CONDITIONS  SIMILAR TT THOSE ACTUALLY  USED
   TO KILL  MOSQUITO LARVAE  AND COMPARE  THE  RESULTS WITH LABORATORY  DATA.
   FE'iTrildN  WAS APPLIED TO A FLORIDA GULF  COAST SALT MARSH  BY  SPRAYING
   THE  WATER  SURFACE   AND ALLOWING  NATURAL   MIXING  TO  DISTRIBUTE  THE
   CHEMICAL  WITHIN THE  SALT  MARSH SYSTEM.  THS FIELD SITE CONSISTED OF  A
   LONG,  NARROW  WATER BODY  OF APPROXIMATELY .5 HECTARES SURROUNDED ON ALL
   SIDES   BY JUMC'JS RCtMEQIANUS  GRASS FLATS WHICH  FLOODED  PERIODICALLY,
   DEFENDING 0!J  THE TIDAL FLUX.  A  NARROW PASSAGE, NORMALLY CONNECTING THE
   MARSH   WITH  SANTA  ROSA   SOUND,  WAS  TEMPORARILY  SEALED  DURING  THE
   PESTICIDE APPLICATION. RHOOAMINE  WT, A  FLUORESCENT DYE WHICH DOES  NOT
   SORB   TO  SEDIMENTS 3R PHOTQLYZE,  WAS ADOEO  SIMULTANEOUSLY  WITH  THE
   FENTHION TO .'1F3SUR5 LOSSES DUE  TO  DILUTION. CONCENTRATIONS OF DYE  AND
   FEMTHION,  AFTER AN  INITIAL  12-HQUR EQUILIBRIUM MIXING TIME,  WERE  50
   MICR3G3AM/L  4MD 25 HICROGSAM/L,  RESPECTIVELY. CONCENTRATIONS OF  80TH
   CHEMICALS, AS MEASURED AT  FIVE  SAMPLING  SITES, DECREASED EXPONENTIALLY
   WITH   TIME, THE FEMTHION DISAPPEARING MORE RAPIDLY THAN THE  DYE.  THE
   HALF-LIFE P03 FENTHIQN,  EXCLUDING  LOSSES DUE TO DILUTION, WAS
   ESTIMATED ftT  25 HOURS. THESE  RATES WERE  FASTER THA^J THOSE OBSERVED  IN
   MICRjCaSM  STUDIES.   PHOTOLYSIS MAY HAVE SEEN PARTLY  RESPONSIBLE  FOR
   THIS   DIFFERENCE. 4 SECOND DOSING  WITH  THE PESTICIDE, WHEN  THE  WATER
   TEMPERATURE WAS 4-5 DEGREES  C LOWER, RESULTED IN LOWER  3IODEGRADATION
   RATES,   SIMILAR  TO THOSE  PREDICTED IN  LABORATORY  STUDIES.  PLEXIGLAS
   BOXES   WERP  PLACED   IN  THE MARSH  TO ISOLATE A SECTION  OF  WATER  AND
   SEDIMENT,  AND  REDUCE LOSSES DUE  TO DILUTION. THESE  BOXES  INDICATED
   LOSS   RATES SIMILAR TO THOSE  NQNDILUTIONAL LOSS RATES OBSERVED IN  THE
   HA IN   ^ATER  BODY. SIGNIFICANT  FENTHION  AND  DYE  CONCENTRATIONS  WERE
   DETECTED  IN  THE SEDIMENTS.  DIFFUSION RATES  (INCLUDING  BIOTURBATION)
   DERIVED   FSOM  MICROCOSM STUDIES  WERE SUFFICIENT TO  ACCOUNT  *OR  THE
   AMOUNT   OF FENTHIO-.1 DETECTED  14 THS  SALT MARSH SEDIMENT.  OUR  RESULTS
   INDICATE THAT DATA FROM  MICR1CDSMS WAS  ESSENTIAL FOR INTERPRETATION OF
   FI5LD   DATA,   3UT  WAS NOT QUANTITATIVELY  SIMILAR TO  RESULTS  IN  THE
   FIELD.  FURTHER EFFORTS ARE NEEDED  TO ACCURATELY ESTABLISH THE  METHODS
   FOR APPLYING  LAFORATDRY  DATA  TO THE  FIELD.

 MURRAY,   =.  DONALD,  AND AL  W.   90URQUIN,   EDITORS.  H74.  DEVELOPMENTS   IN
 INDUSTRIAL   MICRO?I3LOGY,   VOL.   15.   SOCIETY  FOR  INDUSTRIAL  MICROBIOLOGY,
             DC.   426P.   CcRL,G8  244*).
                                   PAGE  27

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NOVICK, NORMAN  J.,  AND MARTIN ALEXANDER.  19*5   ^METABOLISM  OF  LOW
^?CFfTR5pJLN%^T^r°PACHLOR'  ftL^HLOR/IN3'CYc 3 frfSN1  £SAGE° AND  LAKE
WATER.  APPL. ENVIRON, MICKGEIQL.  49(4 ): 737-743.  CERL.G3 X437*>,
   AArHRr?mn*n  - ,           (2-CHLORQ-N-ISOPRDPYL ACETANILIDS)  AND
   ALACHLJR  E2-CHLORO-2 , -j '-D 1 ETHYL-N-C METHQXYM^THYL) ACET ANIL IOE3  WERE
   NOT  MINERALIZED,   CYCLUATE  C S-STHYL-N-ETHYLTHIQCYCLQHEXANECARB AMATE)
   WA5  SLOWLY  OR  NOT MINERALIZED, ANO ANILINE AND  CYCLOHEXYLAMINE  WERE
   READILY   MINERALIZED IN SEWAGE AND LAKE WATER.  PRQPACHL3R,   ALACHLQR,
   AND  CfCLOATE   WERE  EXTENSIVELY METABOLIZED, 3UT  THE   PRODUCTS  WERE
   ORGANIC.   LITTLE CONVERSION OF PRQPACHLOR AND ALACHLOR WAS EVIDENT   IN
   STERILIZED  SEWAGE OR LAKE WATER, THE COMETA30LISM OF  PROPACHLOR   WAS
   ESSENTIALLY   LINEAR  WITH  TIME  IN LAKE WATER AND  WAS  WELL   FIT   BY
   ZE90-CRDER  KINETICS IN SHORT PERIODS ANO 5Y FIRST-ORDER   KINETICS   IN
   LONGER   PERIODS  IM  SEWAGE. THE RATE OF C'IMETABQLISM  IN  SEWAGE   WAS
   DIRECTLY   PROPORTIONAL TO PR3PACHLOR CONCENTRATION AT LEVELS  FROM   63
   PG/ML  TO M03E  THAN 100 NG/ML. GLUCOSE B'JT NOT ANILINE   INCREASED   THE
   YIELD  3F  PRODUCTS  FORMED DURING PROPACHLOR COMETA80LISM  IN SEWAGE.   NO
   MICROORGANISM   ABLE TO USE PROPACHLOR AS A SOLE SOURCE OF  CARSON   AND
   ENERGY WAS ISOLATED, BUT BACTERIA ISOLATED FROM SEWAGE AND LAKE  WATER
   METABOLIZED  THIS CHEMICAL. DURING THE META30LISM OF THIS HERBICIDE   3Y
   TWD  OF   THE BACTERIA, NOME OF TH£ CARSON MAS  ASSIMILATED.   OUR  DATA
   INDICATE  THAT  COMETA3GLI5M OF THESE PESTICIDES TAKES PLACE AT
   CONCENTRATIONS   OF SYNTHETIC COMPOUNDS THAT COMMONLY OCCUR IN   NATURAL
   WATERS.

 O'CONNOR, DONALD  j.»  AND JOHN P. CONNOLLY.  1980.  EFFECT OF  CONCENTRATION  OF
 ADSORBING SOLIDS  IN THE PARTITION COEFFICIENT.  WATER RES.  14( 10) : 1517-1523.
 (ERL,GB 396).

   THE  RESULTS  OF  A  NUMBER OF LABORATORY  STUDIES  ARE  PRESENTED   TO
   DEMONSTRATE  AN  INVERSE RELATIONSHIP BETWEEN CONCENTRATION  OF  AOSOR3IMG
   SOLIDS   AND   PARTITION  COEFFICIENT. VARIOUS  FUNCTIONAL   FORMS  WHICH
   DEFINE   THE   RELATION ARE DEVELOPED AND CORRELATED WITH  THE  DATA.   A
   POWER-LAW  D-PFNOENCE  OF PARTITION COEFFICIENT  ON  CONCENTRATION   OF
   SOLIDS   IS SHOWN,  THE SIGNIFICANCE OF THIS RELATIONSHIP  IN   ASSESSING
   THE  FATE  OF   HYOROPHOBIC  POLLUTANTS IN  NATURAL  WATER  SYSTEMS   IS
   DISCUSSED,

 O'CONNOR,   JOSEPH  M., A.J. LANZA, ALBERT KOLBYE, FRANK G. WILKES,  AND   R03ERT
 J.   PIERC-.   1980.  EXPLORING THE VARIOUS ASPECTS RELATED TO  THE   DUMPING   OF
 DREDGED   SPD1L   MATERIAL  IN  THE  OCEAN  ANO  THE  PCS  CONTAMINATION  ISSUE
 (STATEMENT).  IMS   DR=DGE  SPOIL  DISPOSAL AND  PCB  CONTAMINATION,  HEARINGS
 BEFORE THE  COMMUTE? ON MERCHANT  MARINE AMD FISHERIES, HOUSE  OF
 REPRESENTATIVES,  NINETY-SIXTH CONGRESS, MARCH 14, MAY 21, 1980.  U.S.
 GOVERNMENT   PRINTING OFFICE, WASHINGTON, DC,  SERIAL NO. 96-43.   PP.   507-568.
 CcRL.GB X289#).

   THIS PANEL PRESENTATION IS ON  HUW-! HEALTH IMPACT FROM OCEAN   DISPOSAL
   OF CDNTAMJMATED DREDGE SPOIL.
                                   PAGE   28

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                               POLYCHI-^INATED BIPHENYL TRANSPORT  IN  COASTAL
                           n34~083»   U'S*  =NVI*OMMENTAL  PROTECTION  AGENCY,
                       LABORATORY,  GULF BRE-ZE,  FL.  98?.
                                                  CPCBS) MAY BE
             -c  n  ornc        OIET*R* SOURCES WAS STUDIED  BY  PROVIDING
              r,n-- ^BS  CAS  ftR3CL0^  1254 IN -ODD) TO  STRIPED  BASS  AND
     CT.TTT C^0^-GUT TRANSPORT,  TISSUE DISTRIBUTION  AND  ELIMINATION.
   ASSIMILATION  AMD ELIMINATION  OATft FROM SINGLE AND MULTIPLE DOSES  FOR
   ?1?3^E/ISH W"R€ USE[ T°  CflLCUL^£  RATE-CONSTANTS FOR PCB  ACCUMULATION
   (KA)  AND ELIMINATION CKE)  ACCORDING TO ONE-COMPARTMENT PHARMACOKINETIC
   MODELS.   THF  DATA  FROM  ANALYSIS OF INDIVIDUAL TISSUES  WERE  USED  TO
   CALCULATt KA AND KE -GR  INDIVIDUAL TISSUF COMPARTMENTS. TH~
   PHARMACCKINETIC  DATA  WERE  USED  TO EVALUATE THE  IMPORTANCE  OF  PCB
   UPTAKE  FROM -ODD, ESTIMATED  80DY BURDENS ARISING FROM PCS IN FOOD, AND
   TO  CALCULATE A LQMG-TIRM  MODEL  FOR PC3 ACCUMULATION IN  HUDSON  RIVER
   STSIPED   3S.S3. THE  MAJOR CONCLUSIONS FROM THE STUDY ARE THAT  PCBS  IN
   FOOD REPRESENT A MAJOR SOU3CE  OF PCB TO FISH (UP T3 301 OF TOTAL  BODY
   BURDENS). THE ?>C3S  OBTAINED  "ROM F009 CAUSE A RAPID APPROACH TO STEADY
   STATE,  BUT A*.E ELIMINATED  SLOWLY WITH 4 HALF-TIME OF 120 HR. MORE THAN
   35? OF  THE PCB INGESTED  irflTH FOOO  IS ASSIMILATED INTO THE TISSUES. THE
   LOtMG-TER?1  MODEL  SHOWED THAT  PCS  BURDENS IN STRIPED BASS  EXPOSED  TO
   FOOD  CCNTAINIMG DIFFERENT CONCENTRATIONS OF PCB WILL  DECLINE  SLOWLY
   rfHEN LEVELS IN FQOO DECLINE, BUT INCREASE RABIDLY C90% PLATEAU REACHED
   IN  ^  DOS5S) iJHEN  LEVELS  IN FGGD  INCREASE,  PRELIMINARY  VERIFICATION
   STUDIES  SUPPORT  THE  PHARMACCKINETIC MQOEL FOR  PCB  ACCUMULATION  IN
   STRIPED 3ASS WITH rCOD AS  THE  MAJOR SOURCE.

D'NEIL,  1LLEN J., CAROL  A. MONTI,  PARMELY H. PRITCHARD, AL W, BOURQUIN,   AND
DONALD G.  AHEARN.  1935.   EFFECTS OF  LUGWORMS AND SEAGRASS ON KEPONE
CCHLQRDtCJNE)  DISTRIBUTION IN  SEDIMENT/WATER  LABORATORY  SYSTEMS.  ENVIRON.
T'OXICOL. CH5M.  4C4): 453-453.  CERLiGB 483),

   THE  INFLUENCE 0>= LUGWORMS (ARcNICOLA CRISTATA STIHPSON) AND  SEAGRASS
   (THALASSIA TtSTUDINUM  KOENIG)  ON KCPONE CCHLORDECONE) DISTRIBUTION  IN
   SEDIMENT/WATER SYSTEMS WAS EXAMINED. RADIDLABELED KEPONE WAS
   INTRQDJCEO II TO CONTINUOUS-FLOW  SEOIMENT/W4TER SYSTEMS, AND THE
   OISSCLVED  AND SORBzD CaNCEMTRATIONS OF KEPONE WERE QUANTIFIED. LUGWORM
   ACTIVITY DSCRE4SEO  THE KEPONr  CONCENTRATION IN THE WATER AND INCREASED
   ITS COMC^NTRATION IN THE SEDIMENT. THE PRESENCE OF SEAGRASSES DID  NOT
   APPRECIABLY AFFECT  THE CONCENTRATION Oc KEPONE IN THE WATER.
   dlOTURSATIGN  APPEARED  TO  ^E THE PRIME FACTOR IN  THE  TRANSPORT  OF
   KEPONE  FROM WATER TO SEDIMENT.

PIZZA, JOHN C., A-^0 JOSEPH  M. O'CONNO*.  1933,  PCS DYNAMICS IN HUDSON   RIVER
STRIPED BASS. II. ACCUMULATION  FROM DIETARY SOURCES.  AQUAT. TOXICOL.
3C4):313-327.  CE^L^GB 096).

   YOUNG-OF-YFAR STRIPED  3ASS WERE  ADMINISTERED KNOWN DOSES 0?
   CC14)-LAB£LeO  ARDCL3R  1254 IN  NATURAL FOOD  CGAMMARUS  TIGRINUS)  BY
   GAVAGE.   PCB  ACCUMULATION  FOR   THE  GUT  AMD  ELIMINATION  FROM  THE
   WHGL — 300Y ^£R= DETERMINED EMPIRICALLY FOR SINGLE-DOSE AND
   MUTL-PLE-DOS^ STUHIE5. THF DATA  HAVE BEEN APPLIED TO MODELS DESCRIBING
   ABSORPTION  SITF  KINETICS AMD FLUCTUATIONS IN  WHOLE-BODY  BURDEN  AT
   'STEADY  S'T-'   THOSE   VARIABLES   CRITICAL  OF  THE  CALCULATION  AND
   UNDFRSTAMDIN3 V   BIO ACCUMULATION FACTORS, NAMELY  GROWTH,  METABOLIC
   R"T!,  AND  DOSE, ARE  DISCUS5EO  IN THE CONTEXT 0-  THE  KINETIC  MODEL

   RESULTS.


                                  PAGE  29

-------
pmVCHLQRIN.T'n * ^TPH
^TILlI   JHO  nTcTrn
SAXATILIS.  PH.D. DISSERTATION.
                                  ?'ETICS  ^  DISTRIBUTION  OF  DIETARY
                                  >   IN   H'JDSO'J   RIVER   STRIPED  BASS,  MORONE
                                  NEW YORK  UNIVERSITY.   109P.  (ERL.GB X47S*>.
                                       ACCUMULATION   OF  AROCLOR  1254  BY
                      TM  ,TW             9ASS  R£?.   ASSESSING  THE  SIODEGR ADATION  OF  SEDIMENT
ASSOCIATED  CHEMICALS.  IN:  WORKSHOP  PROCEEDINGS:  TOXICITY AND FATE OF
CHEMICALS IN SEDIMENT.  62P.   (=RL,GB 530).
 PSITCHARD,  P.M.   1934.   FATE AND EFFECTS OF POLLUTANTS:  FATE
 ENVIRONMENTAL   POLLUTANTS.  J.  WATER  POLLUT.  CONTROL  PED.

 CERL,'3E 514),
                                                               OF
                                                                56(6) :718-725
   THE  AUTHOR   PRESENTS  A REVIEW OF THE USE  OF  MICROCOSMS  AND  FIELD
   STUDIES TO VERIFY  PREDICTIONS 'JF F1TE AND TRANSPORT OF TOXIC
   CHEHTCALS. MICROCOSMS ARE LABORATORY SYSTEMS THAT SIMULATE PORTIONS OF
   THS FIELD AND  ALLOW  ITS COMPLEXITY TO BE REPRESENTED IN THE

   LABORATORY.
                                  PAGE  30

-------
           --  ;-;HV,p^   '"*  WAUER' J*C- SpaiN' ftMD A-W'  BOURQU1N.   IN
coccuuarpp  iMnr -S™?ori-   A™ION IN mSP A*° SEDIMENT  TEST  SYSTEMS   ^ROM
FRESHWATER  AND  '::5TU^IN,  ,IT£S.   4PDL. =NVI,ON.  HICPOBIOL.  CERL,G3  513).

   VARIATIONS IM THE  DEGRADATION RATE OF METHYL PARAHION IN A
   iHAKc-.-L^S* TEST WtR-  DETERMINED UNDER ETCTIC AND ASIQTIC  CONDITIONS,
   UbINo  WAT-R  AND  SEDIMENT/WATER SUSPENSIONS  GBTATNED  FROM  THIRTEEN
   aAMPn'JG SIT.S 1,1  TWO  GULF COAST ESTUARIES, VARIABILITY IN DEGRADATION
   RATES AT T*0 SITES,  RANGE  POINT, FL, AND DAVIS BAYOU, MS, WAS ASSESSED
   DV,:R A THRbE-YcAJ?  ?Ex'IOD.  STATISTICAL ANALYSIS OF TH5 RATES  INDICATED
   THAT _3IOL-3GICAL   DEGRADATION OF METHYL PA
-------
                                     IN ?R5P.  MICROCOSM SYSTEM  TO   MODEL  THE
,-_.  ra  ,0.                  AND ?THE^> POLLUTANTS IN LOTIC  STREAM  ECOSYSTEMS.
CtRL,GB *»59).
          nJ!    nx??   r^vc^ DESI5NED TO SIMULATE THE RIFFLE   AND   POOL
            TM^-O?     '^SYSTEM. CONDITIONS OF  NATURAL  TURBULENCE   AND
   ™TT cJ^Mo     " " R ^ PR£SERl/ED- WAT^R C'JLUMM MIXING WAS   OPTIMIZED.
   INTACT SECTIONS  OF  THE STREAM INCLUDING ASSOCIATED P=RIPHYTON,
   MACROPHYTES  AND   INVERTEBRATES WERE TRANSPORTED TD  "MICROCOSMS  USING
   TRAYS.  CALI3RATIOM   Or  THE MICROCOSM'S BEHAVIOR WITH  THE   FIELD  IS
   DEMONSTRATED WITH  STUDIES INVOLVING THE FATE AND EFFECT OF A  TOXICANT,
   P """ C R ™ S J L *

PR1TCHARC,  P.h.   1981.  MODEL ECOSYSTEMS.  IN:  ENVIRONMENTAL  RISK   ANALYSIS
OF  CHEMICALS.  RICHARD  A. CSNvlAY, EDITOR, VAN NOSTRANO  REINHOLD  CO.,   NEW
YORK, NY.  PP. 257-353.  CERL,G3 *24*).

   MICROCOSMS  OP  MODEL ECOSYSTEMS ARE DISCUSSED FOR THEIR   POTENTIAL  IN
   STUDYING  ECOSYSTEM  STRUCTURE AND FUNCTION IN LABORATORY  SYSTEMS   AND
   FOR  THEIR  APPLICATION  TO CHEMICAL RISK  ASSESSMENT.  THE   MICROCOSM
   APPROACH IS REVIEWED A;jD SEVERAL OPERATIONAL CRITERIA ARE SUGGESTED AS
   MEANS OF NARROWING THE SCOPE OF THE APPROACH. EXAMPLES AND INFORMATION
   ON COMPONENT ANALYSIS, SYSTEM DESIGN AND FIELD VALIDATION OF
   MICROCOSMS A^E  PROVIDED TO EMPHASIZE THE ADVANTAGES  AND   DISADVANTAGES
   OF  CERTAIN  !OOEL  ECOSYSTEM STUDIES. THE ROLE OF MICROCOSM STUDIES  IN
   PERFORMING  EFFECTS  ASSESSMENT AMD EXPOSURE CONCENTRATION  ESTIMATIONS
   IS  ALSO  EXPLORED  WITH AN EFFORT  TO  DISTINGUISH  THOSE   LABORATORY
   SYSTEMS  WHICH   GENERATE  INFORMATION FOR THE  PURPOSES   OF   SCREENING
   CHEMICALS as OPPOSED TO DIRECT EXTRAPOLATION TO NATURAL   ENVIRONMENTAL
   SITUATIONS.

PRITCHARD,  PARMCLY H., CAROL A. MONTI, ELLEN J. O'NEILL, JOHN   P.  CONNOLLY,
AND  DONALD  3. A^EARN.  IN PRE3.  MOVEMENT Or KEPONE ACROSS  AN UNDISTURBED
SEDIMENT-WATER  I^TERCACE  IN LABORATORY SYSTEMS.  ENVIRON.  SCI.  £   TECHNOL.
(ERL,G8
   LABORATORY  TEST  SYSTEMS, SUCH AS FLASKS AND MICROCOSMS,  ARE  FREQUENTLY
   USED  TO  EXAMINE THE INTERACTIONS BETWEEN POLLUTANTS AND SEDIMENT.   WE
   STUDIED THE  DISTRIBUTION QF 3ADIOL&8ELED KEPONE DISSOLVED  IN
   CONTINUOUSLY  FLOWING SEAWATER AND ADDED TO A SEDIMENT- WATER  MICROCOSM.
   TriS  SEDIMENT WAS  FRACTIONATED IMT3 LAYERS  AND  THE   SORBED   KEPONE
   CONCENTRATIONS   WERE MEASURED TC DETERMINE TOXICANT  PENETRATION  INTO
   THE SEDIMFNT. Th? DATA  WERE USED TO TEST WHETHER  A MATHEMATICAL MODEL
   BASED ON  IMD6PENOEMT FLASK STUDIES OF THE PROCESSES AFFECTING  THE FATE
   OF KEPQNE COULO  ACCURATELY PREDICT THE DISTRIBUTION OF THE TOXICANT  IN
   THE  MICROCOSM SEDIMENT AND MATES. THE MODEL ACCURATELY  DESCRIBED THE
   OBSERVED  K-P3NE  DISTR I3UTION. MICROCOSMS, 3Y SIMULATING  THE  COMPLEXITY
   QF  NATURAL   ENVIRONMENTS, PROVIDED A USEFUL TOOL  FOR  EVALUATING THE
   ACCURACY  OF  MATHEMATICiL PREDICTIONS CONCERNING THE DISTRIBUTION OF   A
   TOXICANT  IH  AQUATIC  SYSTEMS.
                                  PAGE  32

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                                          -  198-  PERSPECTIVE  ON  THE ROLE OF
        Pi, M.TT,   M-C.O           D EFF^TS ASSESSMENTS.   IN:   CONCEPTS  IN
  ov-  rnM P P   «^SJRt«S^TS.  HARRIS  H.  WHITE,   EDITOR,   UNIVERSITY  OF
MARYLAND, COLLEGE  PARK,  MO.   PR, 115-133,   CERL,GS *63).

   THIS  PAPER  PROVIDES  A  PERSPECTIVE ON  THE  POSSIBLE   INTERFACING  OF
   MICROCOSM STUDIES  WITH BOTH WASTE ASSIMILATORY CAPACITY  DETERMINATIONS
   ANO  OTHER LESS  QUATITATIVE TY^ES DF ASSESSMENT. S1HE  QF THE   PROBLEMS
   AND INCDNSIoTENCIE^  IN THE INTERPRETATION AND APPLICATION OF  MICROCOSM
   RESULTS ARE DISCUSSED. CONCEPTUAL IDEAS  3N HOW MICROCOSMS CAN BE   USED
   IN QUANTITATIVE  ANO  QUALITATIVE RISK ANALYSIS ARE PRESeNTED.  TWO  BASIC
   CRITERIA ARE PROPOSED FOR THE DEVELOPMENT OF THE SCREENING   MICROCOSM:
   A.)  ASSURANCE   THAT THE  SAMS INFORMATION CANNOT BE OBTAINFD   IN   MORE
   SIMPLE,  LABORATORY   SYSTEMS;  B.) ASSURANCE  THAT  IF   THE   SCREENING
   MICROCOSM  RESULT  IS N3T  ECOLOGICALLY UNIQUE, IT IS, AT  LEAST  A   MORE
   SENSITIVE  INDICATOR  OF  TDXTC EFFECTS OR =ATE THAN  OTHER   LABORATORY
   TESTS, ARGUMENTS ARE PRESENTED TO SUPPORT THE CONTENTION THAT
   M1CR2C3S*S,  FROM   A QUANTITATIVE 3ISK ANALYSIS  STANDPOINT,   HAVE  NO
   PREDICTIVE  VALUE  3Y THEMSELVES. THEY ARE INSTEAD,  REPRESENTATIONS  OF
   THE STATe-QF-THE-WHGLE OF CERTAIN ECOSYSTEM SECTIONS WHICH CAN  BE USED
   AS A MEANS QF  VERICYING THE ENVIRONMENTAL SIGNIFICANCE  OF OTHER  TYPES
   OF LABORATORY  DATA AND THE CORRECTNESS Or KINETIC .EXPRESSIONS USED  TO
   DE5CSI3E INDIVIDUAL  FATE  AMD EFFECTS PROCESSES. THE MICROCOSM IS   ALSO
   A  RESEARCH TOOL WHICH C >\H ENHANCE OUR QUANTITATIVE  UNDERSTANDING  OF
   THE  PROCESS   INTERACTIONS AND METABOLIC NETWORKS TYPICAL  OF  NATURAL
   ECOSYSTEMS,

 PRITCHARD, P.H.,  3.J. LARSON, AMD L.S. CLESCERI.  1980.   SYNOPSIS  OF
 DISCUSSION SESSIOM:  EXTRAPOLATION.  IN:  BIOTRANSFORMATION AND  FATE OF
 CHEMICALS  IN THE  AQUATIC ENVIRONMENT,  ALAN W. MAKI,  KENNETH L. DICKSON  AND
 JOHN  CAIRNS, J3,  EDITORS, AMERICAN SOCIETY OF MICROBIOLOGY, WASHINGTON,  DC.
 PP. 99-104.  
-------
       R?-CT :,  i.rr^;  BOURQ(JI^ H.L. rREOSICKSON.  AND  T.  MAZIARZ.   1979.
      -Ovc n    ACTORS  AFFECTING ENVIRONMENTAL FATE STUDIES  IN   MICROCOSMS.
IN:   WORKSHOP:  M^CRGSIAL   DEGRADATION OF POLLUTANTS IN MARIN-  ENVIRONMENTS.
EPA-600/9-79-012, A.W.  30URQUIN AND P.H. PRITCHARD, <=QITO
-------
                                              w.w. WALKER.  1984.
                     ADftTICN RATFS OF PESTICIDES IN WATER/SEDIMENT   SYSTEMS
            -V L i b 3  5 1 5 J •
     nHpTT?*?'-TW?  PU*GICID£S, PIVE ORG4NOPHORPHORUS  INSECTICIDES,
AN'j  OJE  MiriulJt   CACAPICIDE) MERE  CHARACTERIZED  WITH  RESPECT   TO
DEGRADATION  RATS   UNDER BIOTIC AND ABIOTIC  CONDITIONS  IN   ESTUARINE
WATER  AMD   SEDIMENT/WATER SfSTEMS USING A  SIMPLE  SHAKE-FLASK   TEST.
DECAY  RATrS   FOR   EACH CHtMICAL COULD GENERALLY  8E  DESCRIBED   BY   A
FIRST-3ROcR  •-100EL.  THE DEGRADATION Of METHYL PARATHIDN, HOELON,  BRAVO,
3QLSTAR,  CENTHI3N,  ANO 30LERQ WAS BIOLOGICALLY MEDIATCD. THE  FASTEST
3IODEGRA3ATI3N RATES OCCURRED WHEN SEDIMENT WAS PRESENT. THE
DEGRADATION  OF T
-------
RUBINSTtIN,   N.I., c. LORES, AND  M.R.  GREGORY,   1983,   ACCUMULATION  OF  PCS,
MERCURY AMD  CADMIUM BY NEREIS VlRtNS,  MERCENARY  MERC-CNARIA  AND   PALAEMONETES
PUGIO FROM CONTAMINATED HARBOR  SEDIMENTS.   4QUAT.  TOXICQL.  CAMST.).
3C3):249-26Q.  CERL.G3 452).

   ACCUMULATION OF POLYCHLORINATED  SIPHENYLS  CPCSS),  MERCURY,  AND CADMIUM
   3Y  SANDWCSMS CNER5IS VISEMS). HARD CLAMS  
-------
RUBlNSTcPJ,   NORMAN  I.,  W.T.  GILLI4M,  AMD   N.R.   ^RFGORY.   1984.   DIETARY
ACCUMULATION  0? PCBS FROM A CONTAMINATED SEDIMENT SOJRCE  BY  A  DEMERSAL  FISH
(LEIOSTOMJS  XANTH'JRUS).  AQUAT. TOXICJL.  5(4}: 331-34'..  (ERL.GS  485).

   ACCUMULATION  AND  DIETARY TRANSFER  OF PCBS  CRQM   CONTAMINATED  HARBOR
   SEDIMENTS  WERE  STUDIED  IN A  LABORATORY  FOOD  CHAIN  CONSISTING   OF
   SEDIMENTS, POLYCHAETES (NEREIS  VIRENS) AND A PRE9ATQRY  FISH
   CLEIOSTQMUS  XANTH'JRUS).  THE   STUDY  WAS CONDUCTED  IN   TWO   PHASES   TO
   DISTINGUISH  DIETARY  UPTAKE  FROM   PC3  ACCUMULATION   RESULTING  CROM
   SEDIMENT   EX'OSUSE  ALONE.  IN   PHASE  I  FISH  AN3  POLYCHAETES  WERE
   SEPARATELY ExPTSED TO FIELD-COLLECTED PC3 CONTAMINATED SEDIMENTS (5.2
   UG/G  DRY WEIGHT AS AR3CL03 1242  AND  1254) IN  FLOW-THROUGH  SEA-WATER
   SYSTEMS  FOR  40  DAYS  TO ALLOW  ORGANISMS  T3  ATTAIN  STEADY  STATE
   CONCENTRATIONS.  IN PHASE II THE  DIETARY FRACTION  OF PCB  ACCUMULATION
   WAS  DETERMINED BY SELECTIVELY  FEEDING EXPOSED AND  CONTROL   GROUPS   OF
   FISH  OOLYCHAETES  HAVING  A KNOWN PCB BODY  BURDEN.  IN  ADDITION   THE
   EFFECT OF DIRECT SEDIMENT CONTACT ON  PCB ACCUMULATION BY L.  XANTHURUS
   WAS INVESTIGATED. RESULTS DEMONSTRATE TH^T CONTAMINATED SEDIMENTS   CAN
   SERVE  AS -A SOURCE OF PCBS FOR  UPTAKE AND TROPHIC  TRANSFER   IN  MARINE
   SYSTEMS.   FISH EXPOSED TO PCB-CONTAMINATED SEDIMENTS AND FED   A  DAILY
   DIET OF POLYCHAETES FROM THE SAME SEDIMENT ACCUMULATED  MORE  THAN TWICE
   THE  PCB WHOLE-BOD* RESIDUES THAN FISH EXPOSED TO   SIMILAR   CONDITIONS
   BUT  FED U?JCONTAMINATED POLYCHAETES.  THE DIETARY CONTRIBUTION  OF  PCBS
   ACCOUNTED FQ3 53% OF THE TOTAL  BODY  3URD6N MEASURED  IN  FISH  FED  FOR  20
   DAYS,  AND  THIS PERCENTAGE APPEARED  TO  3£   INCREASING.  RESULTS  ALSO
   INDICATE THAT CISH  ISOLATED FROM DIRECT  CONTACT WITH  PCB-CONTAMINATED
   SEDIMENT  DO  MOT   SIGNIFICANTLY CP  LESS   THAN   OR  EQUAL  TO  0.05)
   ACCUMULATE  PCB RESIDUES WHEN COMPARED WITH  FISH ALLOWED CONTACT  WITH
   SEDIMENT.

 RUBINSTEIN,  MORM&N  I.  1978.  EFFECT  OF SODIUM  PENTACHLOROPHENATE   ON   THE
 FEEDING ACTIVITY OF THE LUGWCRM,  4RENICOLA  CRISTATA STIMPSON.   IN:
 PENTACHLOROPHENOL:  CHEMISTRY,  PHARMACOLOGY, AND  ENVIRONMENTAL   TOXICOLOGY.
 K.  RANGA   RAO, EDITOR, PLENUM PRESS, NEW   YORK,  NY.   PP.  175-179.   (ERL,GB
   1*).

   A   BcNTHIC  BIOASSSY  UTILIZING TI'1E-LAPSE   PHOTOGRAPHY WAS  USED   TO
   MEASURE  THE EFFECT  OF  FOUR CONCENTRATIONS OF  NA-PCP (45,  80,  156   AND
   276 UG/L) ON THE FEEDING ACTIVITY OF ARENICOLA CRISTATA. THERE WAS   NO
   MARKED   EFFECT  ON  FEEDING  ACTIVITY  AT 45  UG/L.  NA-PCP SIGNIFICANTLY
   AFFECTED FEEDING ACTIVITY AT CONCENTRATIONS  OF 80,  156, AND  276   IG/L.
   AS  THE  LUGWQRM FEEDS  IT MIXES  ORGANIC MATERIAL AND OXYGENATED   WATER
   INTO  THE SUBSTRATE. INHIBITION OF THIS  ACTIVITY COULD  AFFECT   BENTHIC
   COMMUNITY   TROPHIC   STRUCTURE   AMD   SUBSTRATE-WATER COLUMN   DYNAMICS.
                                  PAGE  37

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RUBINSTEIN,   NORMAN  I., CHARLES  N.  D'ASARO,  CHARNELL  SOMMERS,  AND  FRANK  G.
WILKES.   1930.  t-FECTS OF  CONTAMINATED  SEDIMENTS  ON  REPRESENTATIVE ESTUARINE
SPECIES  AND  DEVELOPING 8ENTHIC  COMMUNITIES.   IN:   CONTAMINANTS  AND SEDIMENTS,
VOL.   It   TRANSPORT,  FATE  AND  CASE  STUDIES.   ROBERT  A.   SAKER,   =OITOR,   ANN
ARBOR SCIENCE PUBLISHERS, ANN ARBOR,  MI.   PP.  445-461,   CERL.GB  406).

   8IOASSAY   TECHNIQUES DEVEL3P-D TO  EXAMINE  ACUTE AND  SLBL^THAL  EFFECTS
   OF  DREDGED  SEDIMENTS   QK   MARINE  LIFE   ARE   DESCRIBED.   RESULTS  ARE
   REPORTED   COR  LABORATORY TESTS CONDUCTED  TO  DETERMINE  SU8LETHAL  AND
   ACUTE  EFFECTS   OF KEPON E-SO 36ED  SEDIMENT  AND  DREDGED  SPOIL   MATERIAL
   FROM THE  JAMES RIVER AMD THE HOUSTON  SHIP  CHANNEL  ON  THE  MYSID SHRIMP,
   MYSIDC^SIS  3AHIA;  OYSTER,   CRASSOSTRf.A   VIRGINICA;   AND  POLYCHAETE,
   ARENIC3LA  CRISTATE.  CRITERIA ESTABLISHED  FOR  THE  STUDY   INCLUDE  CD
   SURVIVAL   0«=  '"1YSIDS;  C2) SHELL   DEPOSITION   AND   BID ACCUMULATION   OF
   CGNTA^S,INANTS; C3) SUBSTRATE-REWORKING  AND  8IQACCUMULATION 3Y  LUGWORMS;
   <4)  RESILIENCY  OF  MACROfAUNAL   ORGANISMS  THAT   SETTLED  ONTO  TEST
   SEDIMENTS CR3M PLANKTONIC LARVAE.

RUBINSTEIN,  N.I., W.T. GILLIAM, AND  N.R.  GREGORY,   1983.  EVALUATION OF THREE
FISH SPECIES AS BIOASSAY ORGANISMS FOR DREDGED MATERIAL  TESTING.
EPA-600/X-83-062, U.S. ENVIRONMENTAL  PROTECTION  AGENCY,  ENVIRONMENTAL
RESEARCH LABORATORY, GULF BREEZE* FL.   22P.

   THE  OBJECTIVE   OF  THIS STUDY WAS  TO   EVALUATE  SEVERAL   MARINE  FISH
   SPECIES IN TER-1S OF THEIR ACUTE SENSITIVITY TO  MODERATELY CONTAMINATED
   SEDIMENTS  AMD THEIR POTENTIAL FOR  BIO ACCUMULATION  OF  POLYCHLQRINATED
   3IPHENYL (PCB),  A UBIQUITOUS ORGANIC  CONTAMINANT,  SEELYE  ET  AL. C1982)
   HAVE  PREVIOUSLY EXAMINED ACCUMULATION OF  CONTAMINANTS  RELEASED  FROM
   DREDGED  SEDIMENTS  IN A FRESHWATER FISH  SPECIES  CPERCA   FLAVESCENS).
   CONSIDERATIONS   FC2 BIOASSAY SPECIES  SELECTION: A  RATIONALE  TO AID   IN
   SELECTION 0= APPROPRIATE BIOASSAY  ORGANISMS WAS DEVELOPED BY  SHU8A   ET
   AL. C1381). THEI2 LIST OF SELECTION FACTORS INCLUDE:  1),  THE   ORGANISM
   IS  FOUND AT, OR IS RELATFO  TO, SPECIES  AT  THE  DISPOSAL SITE; 2).  THE
   ORGANISM   IS  READILY AVAILABLE THROUGHOUT  THE   YEAR,  EITHER  THROUGH
   FIELD  COLLECTION 3R PURCHASING!  3).  A TQXICQLOGICAL  DATA BASE  EXISTS
   FOR  THE  SPECIES;  4),  THE  jRGAMISM  CAN  BE  MAINTAINED  IN   A  HEALTH
   CONDITION  IM  THE LABORATORY*, 5),  THE ORGANISM IS  CULTURA8LE  IN  THE
   LABORATORY;  6). THE ORGANISM OCCURS  OVER  A WIDE GEOGRAPHIC  AREA;  AND
   7).  THE ORGANISM IS ECONOMICALLY  OP  ECOLOGICALLY  IMPORTANT   OR  BOTH.
   ADDITIONAL FACTORS THAT  APDLY TO  SPECIES  SELECTED  FOR  BIOACCUMULATION
   STUDIES  ARE:  THE ORGANISM  SHOULD  ACCUMULATE   THE   POLLUTANT  WITHOUT
   EXCESSIVE MORTALITY AT CONCENTRATIONS  FOUND IN  THE  ENVIRONMENT AND  THE
   ORGANISM  SHOULD  BE  OF ADEQUATE  SIZE  FOR  TISSUE   ANALYSIS  (O.J.H,
   PHILLIPS,  1980). THREE  SPECIES THAT  MEET  THE  SELECTION  CRITERIA  ARE
   THE SHEEPS^AC MINNOW 
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SCHMIDT,   STEVEN  K.,   ANO   MARTIN  ALEXANDER.  1985.   AFFECTS   OF   DISSOLVED
ORGANIC  CARB3N  AND   SECOND  SUBSTRATES ON  THE  8IODEGRADATION  OF  ORGANIC
COMPOUNDS  AT LOW CONCENTRATIONS.  APPL. CNVIRC-M.  MICROBIOL.   49(4):322-827.
(ERL,GB X488*).

   PSEUDDMONAS  ACID-DVORAKS  AND  PSEUDOMQNAS  SP.  STRAIN   ANL  BUT  NOT
   SALMONELLA TYPHIMURIUM GREW IN AN INORGANIC SALTS  SOLUTION.  THE  GROWTH
   OF P.  ACID-OVORANS  IN THIS SOLUTION WAS NOT ENHANCED  3Y THE ADDITION OF
   2.0 UG Or PHFNDL PER LITER, 3UT THE PHENOL WAS MINERALIZED.
   MINERALIZATION   3F   2.0  UG OF PHENOL PER LITER 3Y  P.  ACIDOVORANS  WAS
   DELAYED  16  H   3Y   70 UG OF ACETATE PtR  LITER,   AND  THE   DELAY  WAS
   LENGTHENED  BY INCREASING ACETATE CONCENTRATIONS!  MnSREAS  PHENOL  AND
   ACETATE  WC.P£ UTILIZED SIMULTANEOUSLY AT CONCENTRATIONS OF 2.0  AND   13
   UG/LITER,  RESPECTIVELY.  GROWTH OF PSSUDO^ONAS SP.  IN  THE   INORGANIC
   SALTS  SOLUTION  WAS NOT AFFtCTEO BY THE ADDITION  OF 3.0  UG  EACH   OF
   GLUCOSE  AND  ANILINE  PER LITER, NOR WAS MINERALIZATION  OF  THE  TWO
   CUHPuUMDS  DETECTED  DURING  THE INITIAL PERIOD  OF  GROWTH.  HOWEVER,
   MINERALIZATION QF  30TH SUBSTRATES 3Y THIS ORGANISM OCCURRED
   SIMULTANEOUSLY CURING THE LATTER PHASES OF GROWTH  AND AFTER  GROWTH  HAD
   ENDED AT THE EXPENSE 0-  THE UNCHARACTERIZED DISSOLVED ORGANIC
   COMPOUNDS IN THE SALTS SOLUTION. IN CONTRAST, WHEN PSEUDQMANAS  SP.  WAS
   GROWN  IN THE SALTS SOLUTION SUPPLEMENTED WITH 300 UG EACH OF  GLUCOSE
   ANO   ANlLINEi  TriE   SUGAR  WAS  MINERALIZED  FIRST,  AND  ANILINE  WAS
   MINERALIZED  OMLY   A^TER MUCH OF THE GLUCOSE CARBON  WAS   CONVERTED   TO
   CG2.  S. TYPHIMURIUM FAILED TO MULTIPLY IN THE SALTS  SOLUTION WITH  1.0
   UG  OF GLUCOSE PER  LITER. IT GREW SLIGHTLY BUT MINERALIZED   LITTLE   OF
   THE SUGAR AT 5.0 US/LITER, BUT ITS POPULATION DENSITY ROSE AT 10  UG OF
   5LJCOSE  PER LITER  CR HIGHER, THE HEXOSE COULD BE  MINERALIZED  AT  0.5
   UG/LITER,  HOWEVER, IF THE SOLUTION CONTAINED 5.0  MG OF ARABINOSE  PER
   LITER.  IN  SOLUTIONS WITH THIS ARABINOSt  CONCENTRATION  ANO  GLUCOSE
   LEVELS  TQD  LOW TO SUPPORT GROWTH, THE PERCENTAGE OF  GLUCOSE   CARBON
   INCQRP3RATED  INTO   S.  TYPHIMURIUM CELLS WAS THE  SAMS   AS   WHEN  THE
   BACTERIUM  WAS GROWN IfJ SOLUTIONS WITH HIGH CONCENTRATIONS OF  GLUCOSE
   ALONE. WHEN GLUCOSE WAS THE ONLY CARBON SOURCE FOR S. TYPHIMURIUM,  THE
   PERCENTAGE OF THE  GLUCOSE CARBON ASSIMILATED AND MINERALIZED
   PROGRESSIVELY   DECLINED  AS  THE SUGAR CONCENTRATION  WAS  REDUCED   TO
   LEVELS  APPROACHING TH~ THRESHOLD =OR GROWTH. THESE  RESULTS  INDICATE
   THAT  SECOND SUBSTRATES AND UNCHARACTERIZEO DISSOLVED  ORGANIC   CARBON
   MAY   PLAY  AM  IMP3RTAMT ROLE IN CONTROLLING THE RATE  AND   EXTENT   OF
   3IDDEGRAOATION  Of  ORGANIC COMPOUNDS AT LOW CONCENTRATIONS.
                                  PAGE  39

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SHIMPt   ROBERT  J.,   AND  FREDFPIC K,  P^ASNDe*.  1985.  INFLUENCE   OF  EASILY
DEG'RAOABLt NATURALLY  OCCURRING CARBON SUBSTRATES ON BIODEGRADATIQN  OF
MGNOSUBSTITUTED  PHENOLS   BY   AQUATIC  BACTERIA.  APPL.  -NVIRON.   MICROBIOL.
49(2):394-401.  (ERL»GB X494*).

   THE   INFLUENCE  OF   READILY  DEGRADABLE,  NATURALLY  OCCURRING   CARBON
   SUBSTRATES  ON THE  BIODEGR4DATION OF SEVERAL  MONOSUBSTITUTEO  PHENOLS
   CM-CRESOL,  M-HMINOPHENOL,  P-CHLGRQPHENOL) WAS EXAMINED.   THF  NATURAL
   SUBSTRATE  CLASSES   USED  W5RS AMINO ACIDS,  CARBOHYDRATES,   ANO   FATTY
   ACIDS.  SAMPLES  OF  THE   MICROBIAL  COMMUNITY  ?ROM  LAKE   MICHIE,   A
   MESOTRJPHIC RESERVOIR,  WERE ADAPTED TO DlFFFpENT LEVELS OF
   REPRESENTATIVES FROM EACH  NATURAL SUBSTRATE CLASS IN'CHEMOSTATS.  AFTER
   AN EXTENDED ADAPTATION  PERIOD, THE ABILITY CF THE -MICROBIAL  COMMUNITY
   TO  DEGRADE  THE   MQNOSU3STITUTED PHENOLS ,^AS DETERMINED   8Y  USING   A
   RADIOLABELSD  SU*STRAT~   UPTAKE  AND  MINERALIZATION  METHOD.  SEVERAL
   MICROBIOLOGICAL CHARACTERISTICS 3F THE COMMUNITIES WERE ALSO MEASURED.
   ADAPTATION TQ INCREASING  CONCENTRATIONS OF AMINO ACIOS, CARBOHYDRATES,
   OR  FATTY  ACIDS ENHANCED  THE ABILITY 3F THE  MICROBIAL  COMMUNITY  TO
   DEGRADE  ALL THREE  PHENOLS. THE STIMULATION WAS LARGEST  FOR  M-CRESOL
   ANO  M-AMINOPHENOL.  THE  MECHANISM RESPONSIBLE FOR THE  ENHANCEMENT  OF
   MOMOSU3STITUTE3 PHENOL  METABOLISM WAS 'JOT CLEARLY IDENTIFIED, BUT  THE
   OBSERVATION THAT ADAPTATION TC AMINO ACIDS ALSO INCREASED  THE
   BIODEG3AOATIQN  OF   GLUCOSE  AND,  TO  A  LESSER  EXTENT,  NAPHTHALENE
   SUGGcSTS   A  GENERAL STIMULATION OF MICROBIAL METABOLISM.  THIS   STUDY
   DEMONSTRATES  THAT   PRIOR EXPOSURE TO LABILE, NATURAL  SUBSTRATES  CAN
   SIGNIFICANTLY ENHANCE  THE ABILITY OF AQUATIC MICROBIAL COMMUNITIES  TO
   RESPOND TO XEKOBIOTICS.

SHIMP,  ROBERT,  AND   FREDERIC K.  PFAEND.ER,  1985.  INFLUENCE  OF   NATURALLY
OCCURRING HUMIC ACIOS  ON  3IODEGRADATION OF MONOSU3STITUTED PHENOLS  BY AQUATIC
BACTERIA.  APPL. ENVIRON  MICR03IQL-.  49C 2) .'402-407.  (tRL,GB X493#).

   SAMPLES  0-  THF MICR03IAL COMMUNITY FROM LAKE MICHIE,  A  MESOTROPHIC
   RESERVOIR  IN CEMTRAL  NORTH CAROLINA, WERE ADAPTED TO  VARIOUS   LEVELS
   <100   TO   1,000 UG/LITER)  OF NATURAL HUMIC ACIDS  IN  CHEMOSTATS.  THE
   HUMIC  ACIDS  WERE   EXTRACTED FROM WftTER SAMPLES FRO?^  BLACK  LAKE,   A
   HIGHLY  COLORED  LAKE  IN  THE COASTAL PLAIN OF  NORTH  CAROLINA.   AFTER
   ADAPTATION,  TSE   MICROBIAL COMMUNITY WAS TESTED FOR  ITS  ABILITY  TO
   DEGRACf  THE  -10?40SU5STI TUTED  P.HENCLS  M-CRESQL,  M-AMINOPHENOL,  AND
   P-CHLORO?H=NOL. ADAPTATION TO INCREASING LEVELS OF HUMIC ACIDS
   SIGNIFICANTLY  RFO«JCED   THE ABILITY OF THE  MICROBIAL  COMMUNITIES  TO
   OEoRAD; ALL THREF  =>HENOLS.  THE DECLINE IN 3IODEGRAOATION WAS
   ACCOMPANIED 3Y A D=CREASE  IN THE NUMBER OF SPECIFIC COMPOUND DEGRADERS
   IN  TH? AOAPTF-) COM-UNITIES.  S40^T-TERM EXPOSURE OF THE  COMMUNITY  TO
   INCREASING  LEVELS   OF  HUMIC  ACIDS HAD NO SIGNIFICANT  EFFECT  ON  THE
   ABILITY  Oc  THE COMMUNITY  TO DEGRADE M-CRESOL. THUS  THE  SUPPRESSIVE
   EFFECT  OF  HU1IC  ACIDS  ON  MONOSUBSTITUTEO PHENOL METABOLISM  WAS  THE
   RESULT  OF LON--.-TF3M FXPOSURt ^0 THE HUMIC MATERIALS.  INCREASING  THE
   LEVELS  nF INORGANIC NUTRTENTS FrD TO THE CHEMOSTATS DURING  THE   HUMIC
   ACID ADAPTATION HAD  LITTLE  E^FtCT ON THE SUPPRESSIVE INFLUENCE OF  THE
   HUMIC  ACIDS,  INDICATING  THAT NUTRIENT LIMITATION  WAS  PROBABLY  NOT
   RESPONSISL^  F3R THE METABOLIC SUPPRESSION. THE RESULTS OF   THE   STUDY
   SUGGEST THAT LONG-TERM  EXP3SJRE TO HUMIC ACIDS CAN REDUCE  THE  ABILITY
   OF  MICROBIAL  COMMUNITIES   TO  RESPOND  T3  MONOSUBSTITUT5D  PHENOLS.
                                  PAGE

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SMITH,   N.G.,  A.W. BQURQ'JIN,  S.A.  CROW,  AND O.G.  AHCA*N,  1976.  AFFECT   OF
HEPTACHL03 ON HSXADcCftNE  UTILIZATION 3Y SELECTED FU\'GI.  7N:  DEVELOPMENTS  IN
INDUSTRIAL MICROBIOLOGY,  VOL.  17.   AMERICAN INSTITUTE 0= BIOLOGICAL  SCIENCES,
WASHINGTON,  DC.  PP.  331-335.   CESL.G3 255*).

   VARIOUS  C.3MCN  3F HEPTACHLDR  DISSOLVED IN HEXADFCANE  WERE  ADDED  TO
   CULTURES  Oc 5UMGI  GROWN  IN  Y£ A ST-NITSOSFN 3ASE PREPARED WITH SYNTHETIC
   SEAWATcR   AND  WITH   DSIC'NIZEO   JATER.  CANDIDA  MALTOSA  AND  CANDIDA
   LIPOLYTICA SHQWEO  GREATEST  UTILIZATION 0? HEXADECANE (20-91%)  WHETHER
   HEPTAC1L3R  HAS  PSESE^T  >1R ABSENT.  ISOLATES  -OF  PICHIA  SPARTINEA,
   CL4DOSPORIUM SP.,  CcPHALQSPQRIUM SP.,  AND PENICILLIUM SP. ALSO
   UTILIZED THE HYDROCARBON,  8UT  TO A LESSER EXTENT. SPECIES OF
   KLUYVEROMYCES  FAILED   TO   GROW  WITH HEXAOrCANE AS  A  CARBON  SOURCE.
   COMPARED  WITH LOW CONCN,  HIGH  CONCN OF HEPTACHLOR APPEARED TO HAVE  A
   SLIGHT  STIMULATING  EFFECT  ON  JTILZATION OF HEXADECANE BY C.  MALTOSA,
   BUT HAD NO EFFECT  ^IfH C.  LIPGLYTICA.

SOMERVILLE,  C.C., C.A.  MONTI,  AND  J.C. SPAIN.  1985.  MODIFICATION OF THE 14C
MOST-PRQBA8LE-NUM3ER  METHOD  FOR  USE WITH NQNPOLAR AND  VOLATILE  SUBSTRATES.
APPL. ENVIRON. MICR3BIOL.  49(3):711-713.  CERL,G3 X496).

   A  METHOD  WAS  DEVELOPED  TO ALLOW THE USE OF  VOLATILE  AND  NONPOLAR
   SUBSTRATES IN 14C  MOST-PROeA8Lt-NUMB£R TESTS, NAPHTHALENE OR
   HEXADECANE  .4AS SDRBED TO  FILTER PAPER DISKS AND SUBMERGED IN  MINIMAL
   MEDIUM.  THE  PROC'DUR"  DEDUCED  THE VOLATILIZATION OF  THE  SU3STRATES
   WHILE  ALLOWING  THEM  TO REMAIN  AVAILABLE FOR  MICR03IAL  DEGRADATION.

SPAIN,  JIM  C., AND  P.A. VAN  VELD.  1983.  ADAPTATION OF  NATURAL   MICR08IAL
COMMUNITIES TO DEGRADATION  OF  XENOBIQTIC  COMPOUNDS:  EFFECTS OF
CONCENTRATION,  IMOCULUM, AMD  CHEMICAL STRUCTURE.  APPL. ENVIRON.  MICROBIQL.
45(2):423-435.  (ERL,GB  440*).
AVAIL. ?=R3M NTIS, SPRINGFIELD, VA:   P383-194522.

   ADAPTATION  OF MICR03IAL POPULATIONS TO DEGRADE  XENOBIOTIC  COMPOUNDS
   FASTER  AFTE3  EXPOSURE   TO THE  COMPOUND  WAS  STUDIED  IN  ECO-CORES.
   RAOIOLABEL'D TEST  CC.MP3UNDS ViESE ADDHD TO CORES THAT CONTAINED NATURAL
   WATER AMD SEDIMENT.  ADAPTATION  WAS DETECTED BY COMPARING
   MINERALIZATION RATES  G2  DISAPPEARANCE  OF PARENT COMPOUND IN
   PR:—EXPOSED AND UNHX^OSEO  CORES. MICROBIAL POPULATIONS IN  PRE-EXPOSED
   CORES  FROM A NUMBER  OF  FRESHWATER SAMPLING SITES ADAPTED  TO  DEGRADE
   P-NITROPHENOL  FASTED; POPULATIONS FROM ESTUARINE OR MARINE SITES  DID
   NOT  SHOW  ANY  INCREASE  IN  RATES OF  DEGRADATION  AS  A  RESULT  OF
   PRE-EXPOSU'RE. ADAPTATION WAS MAXIMAL AFTER TWO WEEKS AND NOT
   DETECTABLE  AFTE?  SIX  WEEKS. A  THRESHOLD CONCENTRATION OF 10  ?PB  WAS
   NOTED, BELOW WHICH NO  ADAPTATION WAS DETECTED. WITH CONCENTRATIONS  OF
   20 TO 100 ?P8» THE BIOOEGRAD4TION RATES IN PRE-EXPOSED CORES WERE MUCH
   HIGHrR  THAN  IN   CONTROL   CuRcS  AND   WERE  PROPORTIONAL  TO  RESPIKE
   CONCENTRATION.  IN   ADDITION,   TRI?LUPALIN,  2,4-DICHLOROPHENOXYACETIC
   ACID (2,4-0) AND P-CRESOL  WERE  TeSTEO  TO DETERMINE WHETHER
   PR=-EX?OSU«E A-F-CTED  SUBSEQUENT BID-DEGRADATION. MICROSIAL POPULATIONS
   DID NOT ADAPT TO T3IFLURALIN.  ADAPTATION TO 2,4-3 WAS SIMILAR TO  THAT
   WITH NITOPHEfJOL. P-CRESOL  WAS  MINERALIZED RAPIDLY IN BOTH PRE-EXPQSURE
   AND UNEXPOSED POPULATIONS,
                                        41

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SPAIN,   J.C., AND C.C.  SOMERVILLE.  IN PRESS. BI03EGRADATION  OF  J^T  FUEL  BY
AQUATIC MICRCBIAL COMMUNITIES,  IN:  PROCEEDINGS:  2ND  INTERNATIONAL
SYMPOSIUM  ON  1ICR38IAL-tNHAlMC£D  CIL RECOVERY,   GEORGIA   STATE   UNIVERSITY,
ATLANTA,  G4, AUGUST  16,  1934.  GEORGIA STATE UNIVERSITY,  ATLANTA,   GA.   23P.
(ERL.GB X4S5),

   THIS  PAPE? DESCRIBES  LABORATORY EXPERIMENTS THAT  STUDIED  THE  FATE  OF
   JET   FUEL IN SEVERAL TYPES OF SITUATIONS THAT COULD  3E  ENCOUNTERED  IN
   THc  FIELD. BENZENE,  TOLUENE, AMD P-XYLENE WERE  THF ONLY  COMPONENTS  OF
   THE   FUEL THAT DISSOLVED IN THE WATER TO  SIGNIFICANT   CONCENTRATIONS.
   ALL  TH3EE COMPOUNDS  VOLATILIZED WITHIN 24 H AND, THUS,  DID  NOT  REMAIN
   IN  THE  WATER LON'5  ENOUGH FOR MICROBIAL DEGRADATION TO  AFFECT   THEIR
   FATE.  INCLUSION  0=  SEDIMENT (500 MG/L DRY WEIGHT) DID  NOT  RETARD  THE
   DISAPPEARANCE  3F  THE FUEL COMPONENTS, AND "ATES OF DISAPPEARANCE  WERE
   IDENTICAL IN CONTROLS  STERILIZED WITH HGCL2,

SPAIN,   J.C.,  *.<\.   VAN  VOLD, C.4. MONTI, P.H. PRITCHARD,  AND   C.R.  CRIPE.
1984.  COMPARISON   OF  o-MITROPHENQL BIQDEGRADATI3N IN  FIELD   AND  LABORATORY
TEST SYSTEMS.  AP»L,  ENVIRON. MICR05IOL.  43(5) : 944-9 50.   CERL.GB 506).

   ACCLIMATION  Or  MICROBIAL COMMUNITIES EXPOSED TO   P-NITROPHENOL   (PNP)
   WAS  MEASURED  IN LABORATORY TEST SYSTEMS AND IN   A  FRESHWATER   POND.
   LABORATORY  TESTS  WERE CONDUCTED IN SHAKE FLASKS  WITH  WATER,   SHAKE
   -L4SKS WITH WATE? AND SEDIMENT, SCO-CORES, AND  TWO SIZES OF MICROCOSM.
   THE  SEDIMENT A^D WATER SAMPLES USED IN THE LABORATORY EXPERIMENTS WERE
   OBTAINED   =Ri3M   TH£  PQMD. AFTER A 6-DAY ACCLIMATION  PERIOD,   PNP  WAS
   iilODrG^AOEO RAPIDLY  IN THE PGNO. WHEN THc POND  WAS TREATED  WITH  PNP  A
   SECOND TIMC, BIOOEGRAD4TION 3EGAN IMMEDIATELY.  THE ACCLIMATION PERIODS
   IN   LABORATORY   TEST SYSTEMS THAT CONTAINED SEDIMENT WERE   SIMILAR  TO
   THAT  IM  THE POi^D, THE ACCLIMATION PERIOD WAS THREEFOLD  LONGER  IN SHAKE
   FLASKS WITHOUT  SEDIMENT. PNP WAS BIOOEGRADED MORE  SLOWLY BY  MICROBIAL
   COMMUNITIES ACCLIMATED IN THE LABORATORY THAN IT WAS IN  THE POND,  AND
   THE  SATE  OF  3IODEGRA3ATION VARIED WIH THE TY^E  OF  TEST,  THE NUMBER  OF
   BACTERIA  A-3LE  TO MINERALIZE ?N? INCPEASEO 3Y 3  ORDERS OF MAGNITUDE  IN
   THE  ?0>JO  DURING  THE  ACCLIMATION PERIOD. SIMILAR INCREASES   ACCOMPANIED
   ACCLIMATION IN  THE LABORATORY SYSTEMS.
                                   PAGE   42

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SPAIN,   J.C.,  C.C.   SOMtRVILLE,  T.J. LEE, L.C. BUTLER,  AND  A.U.   BDURQUIN.
1383.  DEGRADATION «1F  JET  FUEL  HYDROCARBONS BY AQUATIC MICROBIAL COMMUNITIES:
AfJ  INTERIM REPORT 23  OCTOBER 1981 TO 30  SEPTEMBER  1932,  EPA-600/X-83-059t
U.S. ENVIRONMENTAL PROTECTION A3ENCY, ENVIRONMENTAL RFSCARCH LABORATORY,  GULF
BREEZE, FL.  ?05P.                                    " ~

   A  MODEL FUEL MIXTURE  OF  FIFTEEN HYDROCARBONS REPRESENTATIVE OF   THOSE
   DISTILLATE  JfcT   FUELS  WAS USED TO DETERMINE  WHETHER  DEGRADATION   3Y
   NATURAL  MICR09IAL   COMMUNITIES COULD AFFECT THE PERSISTENCE  OF  SUCH
   FUELS RELEASED  IN  AQUATIC ENVIRONMENTS.  THE MIXTURE INCLUDED  HEXANE,
   CYCLOHEXANE, N-HEPTANE,  METHYLCYCLOHPXANF, TOLUENE, N-OCTANE,
   ETriYLCYCLDHEXANE,  P-XYLENE,  CUHENE, TRIM5THYLBENZENE, INOAN,
   NAPHTHALENE, N-T ETR AOECANE,  2f3-OHETHYLNAPHTHALENE. THE WATER SOLUBLE
   FRACTION OF THE MODEL  ~UEL WAS INCUBATED l:j SHAKE FLASKS WITH WATER  OR
   WATER  AND SEDIMENT SUSPENSIONS COLLECTED AT ESTUA3INE AND  FRESHWATER
   SITES. SURFACES FILMS  OF  THE MODEL MIXTURE WERE STUDIED UNDER 3UIESENT
   INCU3ATION. THE DISAPPEARANCE OF HYDROCARBONS WAS MEASURED BY
   CAPILLARY  C3LUMN  SAS  CHROMAT03RAPHY. CONTROL =LASKS  WERE  STERILIZED
    WITH  HGCLC2)  TO  ESTIMATE LOSSES DUE TO ABIOTIC  PROCESSES.  CC6)-CC9)
   COMPOUNDS VOLATILIZED  1UICKLY. INDAN, NAPHTHALENE, AND
   2-f-IETHYLNAPHTHALENE WERE  MUCH LESS VOLATILE 4N9 WERE BIODEGRADED  FROM
    SOLUTION  AFTER   AM INITIAL 244 LAG PERIOD, THE PRESENCE  OF  SEDIMENT
    ASSOCIATED MICROFLORA  SIMULATED DEGRADATION. BIODEGRADATION WAS NOT  AN
    IMPORTANT  FATE PROCESS OF THE MODEL FUEL COMPONENTS IN THE  QUIESCENT
    TEST.   ASSAYS  OF  TOTAL HETEROTRQPHS AND  HYDROCARBONOCLASTIC  BACTERIA
    INDICATED  AN   INITIAL  TOXICITY OF THE FUEL  MIXTURE  FOLLOWED   BY   A
    STIMULATION OF  HYDROCARBON-DEGRADING BACTERIA. FATE TESTS WERE
    REPEATED  WITH  P£TROLEUM-OERIVcD JP-4. THE SOLUBLE COMPONENTS OF  JP-4
    VOLATILIZED  T30   RAPIDLY ^O1? SIODcGRADATION TO  OCCUR.  SEDIMENTATION
    DRAMATICALLY   AFFECTED THE FATS OF FUEL COMPONENTS WHEN! MIXING OF THE
    HYDROCARBON AND SEDIMENT  LAYERS STUDIED. SEDIMENT ASSOCIATED COMPOUNDS
    WtRE  MORE RESISTANT TO VDLATILIZ4TICN AMD MICROBIAL ATTACK.
    SUBSTITUTED  BENZENES  AND N-ALKANES MERE RAOILY 8IODEGRADEO  WHEN NOT
    LIMITED BY EVAPORATION AND SEDIMENTATION. JP-4 DID NOT PROVE TOXIC   TO
    THE   MICROBIAL  COMMUNITIES OF THE TEST SYSTEMS, 3UT DID STIMULATE THE
    REPLICATON 0?  HYOROCARBONOCLASTIC BACTERIA.
                                  PAGE  43

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SPAIN,  jri C., P.H. PRITCdARD,  AND A.M. BOURQUIN.  1980.  EFFECTS  OF
ADAPTATION ON BICDE GRADATION RATES IN S3DIMENT/MATER CORES FROM  ESTUARINE  AND
FRESHWATER ENVIRONMENTS,   APPL.  ENVIRON.  MICS03I3L.  40C4):726-734.   (ERL.GB
410*).

   EXPERIMENTS WERE DEVISED TO  DETERMINE WHETHER EXPOSURE TO  XENOBIOTICS
   WOULO  CAUSE MICR03IAL  POPULATIONS TO DEGR4D= WITH THE COMPOUNDS   MORE
   RAPIDLY DURING  SUBSEQUENT EXPOSURES. STUDIES WcRE DONE WITH
   WATER/SEDIMENT  SYSTEMS  (ECO-CORES)  TAKEN PROM A SALT  MARSH   AND   A
   RIVES.  SYSTEMS  WERE   TESTED FQ% ADAPTATION TO  THE  MODEL   COMPOUNDS
   METHYL  PA2ATHIOM  AND  P-NITRQPHE,«!OL. 14C02 RELEASED  FROM  RADIOACTIVE
   PARENT  CCHPOUMDS   WAS   USED AS A  MEASURE  OF  MINERALIZATION.  RIVER
   POPULATIONS  PRE-EXPOSZD TO  P-'JITR3PHENOL AT CONCENTRATIONS AS  LOW   AS
   60 MG/L DEGRADED THE  NIT^O^HENOL MUCH FASTER THAN CONTROL POPULATIONS.
   RIVER  POPULATIONS   PRE-EXPOSEO TO METHYL »ARATHION  ALSO  ADAPTED   TO
   DEGRADE  THE P2STICIOES MORE RAPIDLY, 3UT HIGHER  CONCENTRATIONS   WERE
   REQUIRED.  SALT  MARSH   POPULATIONS 013 NOT ADAPT  TO  DEGRADE   METHYL
   PARATHIOM.  P-NITR3PHF.NQL-DEGRADING BACTERIA WERE ISOLATED FROM  RIVER
   SAMPLES, BUT NOT FROM  SALT MARSH SAMPLES. NUMBERS OF
   NITROPHEMOL-DE5RADING   BACTERIA INCREASED ^ JO 5 ORDERS  OF   MAGNITUDE
   DURING ADAPTATION.  RESULTS INDICATE THAT THE ABILITY OF POPULATIONS  TO
   ADAPT  DEPEMDS  ON THE  PRESENCE OF SPECIFIC MICOORGANISMS.
   3IODECSADATION  RATES  1,'J LABORATORY SYSTEMS CAN BE AFFECTED BY
   CONCENTRATION   AMD   PRIOR  EXPOSURE!  THEREFORE,  ADAPTATION  MUST   3E
   CONSIDERED  WHEN   SUCH   SYSTEMS  ARE  USED  TO  PREDICT  THE  FATE   OF
   XEN03IOTICS IN  THE  ENVIRONMENT.

 SPAIN,   J.C., AMD  C.C. SOMERVILLE.  1985.  FATE AMD TOXICITY OF  HIGH   DENSITY
 MISSILE  FUELS RJ-5 ANO JP-9 IN  AQUATIC TEST SYSTEMS.  CHEMQSPHERE.
 14(25:239-248.  CERL.GE  X486*).

   THE   HIGH  DENSITY  MISSILE FUELS RJ-5 AND JP-9 RESISTED  BIODSGRADATION
   WHEN  INCU81T.ED  WITH WATER/SEDIMENT SUSPENSIONS COLLECTED FROM   AQUATIC
   HA3ITATS.  3J-5  AMD  JP-9 WERE NOT TOXIC TO THE HICROBIAL COMMUNITIES  AT
   CONCENTRATIONS  OF  400  MG ^ER LITER, BUT RJ-5 WAS TOXIC TO  MYSIDOPSIS
   BAHIA  IN 96-HOUR ACUTE  TESTS 
-------
SUMMERS,  MAX.  1984.   PATHOLOGIC,  BIOCHEMICAL AMD GENT-TIC  PROSES  DEVELOPED TO
DETECT BIOLOGICAL CONTROL  AGENTS IN NON-TARGET HOSTS.  EPA-600/X-84-348,  U.S.
ENVIRONMENTAL  PROTECTION   AGENCY. ENVIRONMENTAL  R«=SrARC*  LABORATORY,   GULF
BREEZE,  FL.  ZIP.

   THE 'JUCLcAR POLYHEOROSIS  VIRUS  OF AUTOGR4PHA CALIFORNIA (ACMNPV)   HAS
   POTENTIAL  USE AS  A  VIRAL INSECTICIDE, ESPECIALLY IN VIEW OF ITS   WIDE
   HOST  RANGE AND LETHAL  EFFECTS  IN LEPIOGPTERA AND HYMENOPTERA   (KELLY,
   1932). IP THE HOST  RANGE  OF 4CNNPV EXTENDS BEYOND INSECTS, ITS  USE  AS
   AN  INSECTICIDE WOULD 3E  COMPROMISED. WF INVESTIGATED THE  ABILITY  OF
   ACMNPV  TO  INFECT  THREE  PDIKILOTHER'-UC VERTEBRATE CELL  LINES  AND A
   NCNPERMIS5IVP INJECT CELL LIME  BY US5 OF HIGHLY SENSITIV* NUCLEIC  5CID
   PROBE  TECHNIQUES   A.NO  ELECTRON MICROSCOPY.  THE  ELECTRON  MICROSCOPY
   STUDIES REVEALED  THAT NUMEROUS  VIRUS PARTICLES ENT~R=D THE  VERTEBRATE
   CELLS ANO NUCLEOCAPSIDS MERE OBSERVED TO PENETRATE TG THE NUCLEUS.  THE
   NUCLEIC  ACID  HYBRIDIZATION STUDIES SHOWED THAT VIRAL  DMA  COULD  BE
   DETECTED IN THr NUCLEI  OF EVERY CELL LINE AFTER EXPOSURE TO ACMNPV, WE
   CONCLUDE THAT, UPOM  EXPOSURE TO ACMNPV, ^N EFFICIENT, TRANSIENT  ENTRY
   OF  VIRUS OCCURS  IN  ALL TESTED  CELL LINES. WHEN EITHER THE  VERTEBRATE
   OR THE NCNPE3MISSIVE INSECT CELLS HERE EXPOSED TO ACMNPV THERE  WftS  NO
   DETECTABLE  PRODUCTIVE   INFECTION, CYTOLOGICAL  CHANGE,  SYNTHESIS  OF
   VIRAL 2Nfl TRANSCRIPTS,  OR PERSISTENCE OF VIRAL DMA.

VAN  VELD, P.*., AND  J.C.  SPAIN.  1983.  DEGRADATION OF  SELECTED  XEN08IQTIC
COMPOUNDS I'J THREE TYPES OF  AQUATIC TEST SYSTEMS.  CHEMOSPHERE.
12(9/10):i291-1305.   C£3L,GS 473).

   THE   SIQDEGRACATIOM  RATES  OF   P-NITROPHENOL,  METHYL  PARATHION   AND
   P-CRESDL WERE COMPARED  IfJ TEST  SYSTEMS COMPOSED OF SEDIMENT AND  WATER
   COLLECTED  F30,>)   VARIOUS   ESTUAR.INE SITES.  P-NITROPHENOL  AND  METHYL
   PARATHION  DEGRADATION   WAS  FASTEST IV  INTACT  SEDIMENT/WATER  CORES
   FOLLOWED  3Y  SEDIMENT-WATER SHAKE FLASKS ^ND SLOWEST IN  WATER  SHAKE
   FLASKS. P-CRESDL  DEGRADED RAPIDLY IN ALL TSST SYSTEMS. THE
   APPLICA3LILITY OF  a  FIRST-3ROER KINETIC MODEL TO DESCRIBE TH£
   DEGRADATION  0~ THESE COMPOUNDS WAS EXAMINED.

WALKER,  W.W,,  C.R.   CRIPE, P.H.  PRITCHARD, ANO  A.W,  BOURQUIN,  IN  PRESS.
BIOLOGICAL AND 4»ICTIC  DEGRADATION! RATFS OF XENOBIOTIC CHEMICALS  IN IN VITRO
ESTUARINE  AND SEDIMENT/WATER SYSTE'-IS-  J. AG^IC. FQCD  CHEM.  CERL,GB 504).
   THREE HERP.ICIDES,  TWO FUNGICIDES, POUR ORG4NOPHORPHORUS   INSECTICIDES,
   AND  CKJE   SUICIDE  CACARICIDE) WERE  CHARACTERIZED  WITH  RESPECT   TO
   DEGRADATION  "ATE  I M  ESTUARINE WATER flND SEDIMENT/WATER SYSTEMS  USING A
   SIMPLE SHAKE  FLASK TEST.  DECAY RATES FDR E4CH CHEMICAL COULD  GENERALLY
   3E DESCRIBED  BY  A  FIRST ORDER MODEL. THE DEGRADATION OF  HO=L3N,  BRAVO,
   60LSTAR,   FEMTHIQN,  AND BOLERO WAS BIOLOGICALLY MEDIATED. THE  FASTEST
   3I2D-GRADATION RATES  OCCURRED WHEN SEDIMENT WAS PRESENT.  THE
   DEGRADATION  OF TRI-LURALIN, DURSBAN, PHORATE, EPN  AND
   PENTACHL3RONITP03FNZFNE  WERE PRIMARILY 3Y A3IDTIC WEANS. RELATIVE   TO
   THF  OTHEP T^ST  MATERIALS, PHQRATE REFLECTED INTERMEDIATE  DEGRADATION
   SATES.  VARIABILITY   IN RATES =ROM REPLICATE FLASKS SUGGESTED  THAT  A
   DIFFCR-NCE IN RATE WITHIN TREATMENTS (STERILE/ACTIVE, WITH AND  WITHOUT
   SEDIMENTS)   3F A FACTOR OF TWO OK LESS WAS P3Q3A3LY  NOT   SIGNIFICANT.
                                  PAGE  45

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WALKER,   WILLIAM  W.  1984.  DEVELOPMENT  TF  A  FATE/TOXICITY   SCREENING  TEST,
EPA-600/4-84-Q74, U.S. ENVIRONMENTAL  PROTECTION  AGENCY.  ENVIRONMENTAL
RESEARCH  LABORATORY, 3ULF BREEZE,  FL.   3QP,

   A  SHAKE-FLASK  SCREENING TEST  WAS  DESIGNED TO   RAPIDLY   EVALUATE  THE
   RELATIVE  JFGS4DATIQN  RATES   OF  A  WIDE  SPECTRUM   OF   CHFMICALS,   EACH
   COMPARED  TO METHYL PASATHION.  TEST  CHEMICALS EVALUATED   WERC   BOLERO,
   BRAVO, DIBUTYLPHTHALATE, OIMILIN,  OURSSA'!,  ENDQSULrAM, HOELON,
   PENTACHLOROBv.NZE.ME,  PHORAfE,   AND   TRIFLU3ALIN.   DIVERSE  REGIMES  OF
   SALINITY, PH, TQC, AMD MICROflHL  BICMASS  WERE ENCOUNTERED ACROSS  SPACE
   ANJ TIME. THE EXPERIMENTAL  DESIGN  FDR  THE SCREENING TEST  EMBODIES FOUR
   TREATMENTS:  ACTIVE  SEDIMENT,   STERILE  SEDIMENT,  ACTIVE  WATER,  AND
   STERILE-  W5TER.  OEC^Y   CURVES  WSRE  PRODUCED  AND   RATE  CONSTANTS  AND
   HALF-LIFE  VALUES  DETERMINE*").  HAL—LIFE  VALUES  FQ* THE   10  CHEMICALS
   EVALUATED VARIED SUBSTANTIALLY  WITH  TIME  AMD  GEOGRAPHIC SAMPLING  SITE.
   IN  ACTIV^ S/STFMS, 3  OF THE  10 CHEMICALS DEGRADED MORE   RAPIDLY   THAN
   METHYL PARATHION. MINE DIBUTYLPHTHALATE  SCREENS  WERE  RUN  INVOLVING SIX
   GEOGRAPHIC   SITES. DISAPPEARANCE  WAS QUITE  RAPID  IN ACTIVE  TREATMENTS
   IN ALL SCREENS.  DISAPPEARANCE  CURVES DESCRIBING  OEP ABATEMENT   EITHER:
   (1)  APPEARED TO BE SUBSTRATE  DEPENDENT  WITH  THE  RATE OF  DEGRADATION
   DECREASING AS 30° WAS  DEPLETED; C2)  APPE4R=D  INDEPENDENT  OF  SUBSTRATE
   CONCENTRATION; OR o>  RE^LECTEO A  MARKED  INCREASE  IN  DEGRADATION   RATE
   DURING THE SCREENING PERIOD.

 WALKER,  WILLIAM  W., C.R.  CRIPS,  P.H,  PRITCHARD,  AND A.W.   30URQUIN.  1984,
 DIBUTYLPHTHALATE DEGRADATION IN  ESTUARINE AND  FRESHWATER SITES.   CHEMQSPHERE,
 13(12):1233-1294.   (E3L,GB  509).

   3IOTIC   AND  ABIOTIC DEGRADATION OF  DI-NJ-3UTYLPHTHALATE 
-------
WALKER,   WILLIAM  W.   1973.   INSECTICIDE PERSISTENCE IN NATURAL   SEAWATER  AS
AFFECTED  BY  SALINITY,  TEMPERATURE, AND  STERILITY.   ^PA-6QO/3-78-044,   U.S.
ENVIRONMENTAL  PROTECTION   AGENCY, ENVIRONMENTAL  RES-ARCH   LABORATORY,   GULF
BREEZE,  FL.  25P.

   THE EFFECT 0- TEMPcRATJR5,  SALINITY, AND STERILITY  ON THE   DEGRADATION
   OF MALATHIQN, OARATHIDN,  METHYL PARATHION, DIAZINDN, AND   ^ETHOXYCHLOR
   IN  ERESH  flNO ESTUASINE  WATER HAS BEEN  DETERMINED  UNDFR  CONTROLLED
   LABORATORY CONDITIONS.  SURFACE WflTER SAMPLES OF 1,  10, 20,  AND  28   PPT
   SALINITY WERE AMENDED WITH  THE ABOVE INSECTICIDES AND INCUBATED  IN  THE
   DARK  AT  30,  20,   AND 1C  DEGREES  C  UNDER  STERILE  AND  NONSTERILE
   CONDITIONS.  INSECTICIDE   ABATEMENT WAS =QLLQWED  3Y  ELECTRON-CAPTURE
   GAS-LIQUID  CH.RGMATCGRAPHie  TECHNIQUES.  MO  SIGNIFICANT   DIFFERENCES
   BETWEEN STERILE  AN3 NONSTERILE TREATMENTS K-JEfiE OBSERVED FOR ANY  OF  THE
   INSECTICIDES  STUDIES,  WHILE THE EFFECT OF INCREASING TEMPERATURE   WAS
   HIGHLY SIGNICICANT  WITH RE3A'!D TO INCREASED DEGRADATION OF  HALATHION,
   PARATHIOM, METHYL  PARATHION, AND OIAZINON. METHQKYCHLQR REFLECTED   THE
   RECALCITRANCE CHARACTERISTIC OF THE CHLORINATED HYDROCARBON
   INSECTICIDES THROUGHOUT 84  DAYS ON INCUBATION AND WAS NOT
   SIGNIFICANTLY AFFECTED  6Y SALINITY, TEMPERATURE, OR STERILITY.
   SALINITY  EFFECTS  WERE  VARIED AMONG THE FOUR  ORGANOPHQSPHATES,  BEING
   HIGHLY SIGNIFICANT  FDR  MALATHICN AMD DIAZINQN, SIGNIFICANT  FOR   METHYL
   PARATHION, AMD NOT  SIGNIFICANT FOR PARATHION.

 UANG, YEI-SHUNG, EUGEME L. MADS^N, AND MARTIN ALEXANDER.  IN  PRESS.
 BIODEGRADATION  BY  MINERALIZATION  OR COMETA30LISM  DETERMINED   BY  CHEMICAL
 CONCENTRATION AND ENVIRONMENT.  APPL. ENVIRON. MICROBIOL.  17P.   CERL,G8
 X489).


 WANG,  YEI-SHUNG,   R.V. SU33A-RAO, AN3  MARTI4  ALEXANDER.   1984.   EFFECT  OF
 SUBSTRATE CONCENTRATION AND  ORGANIC AND INORGANIC COMPOUNDS  ON THE  OCCURRENCE
 AND   RATE  OF   MINERALIZATION  AND  COMETA3CLISM.  APPL.  ENVIRON.   MICROBIOL.
 47<6):il95-1200.  
-------
KEYWORD TITLE INDEX
      PAG:  43

-------
                            KEYWORD  TITLE  INDEX                          P   I
                                                                         A   T
                                                                         G   E
                                                                         £   M
                                      A
ABIOTIC  DEGRADATION! RATES OF XfNOBIQTIC  CHEMICALS  IN IN VITRO ESTUARIN  45- 3
        FACTORS EFFECTING SORPTMr.  OF TOXIC  CQ'-IPOUNDS TO NATURAL SEDIM  14- 1
ACCUMULATION OF PCS, MERCIKY AMD CADMIUM Bf  NEREIS VIRCNS.  MERCENARIA   36- 1
     "        OF °C^S FR°M A CONTAMINATED SEDIMENT  SOURCE BY A DEMERSAL  37- 1
     "        FROM DIETARY SOURCES  /.PC3  DYNAMICS  IN HUDSON  RIVER STRIP  29- 3
ACID  CHARACTERIZATIONS OF SELECTED  SULFATE-REDUCING BACT-RIA AND S?DIM  20- 1
 »   METAB3LISM 9Y THREE AQUATIC BACTERIA  ISOLATED FROM CONTINUOUS CUL  26- 1
ACIDS 3N 6TODEGRADATIOM OF MONQSUBSTITJTED PHENOLS BY AQUATIC 3ACT?RIA  40- 2
ACROSS  AN UNDISTURBED SEDIMENT-WATER INTERFACE  IN  LABORATORY SYSTEMS /  32- 3
ADAPTATION OF NATURAL MICROBIAL COMMUNITIES  TO  DEGRADATION  OF XENOBIQT  41- 3
    11      ON 3I1DEG3AOATION RATES  IN SEDIMENT/WATER CORES  FROM ESTUAR  44- 1
ADAPTED Tu LOW NUTRIcNT CONDITIONS  I'M LAKE ONTARIO /, CHARACTERISTICS 0  25- 1
ADSORBING SOLIDS ON THE PARTITION  COEFFICIENT  /,EFFECT OF CQNCENTRATIO  28- 2
ADSORPTION PROCEDURE /.DENSITIES OF  HACTERIA AND  FUNGI IN COASTAL SURF  18- 3
    "      DESCRIPTOR IN EXPOSURE  CONCENTRATIONS  PREDICTIONS: STUDIES   16- 1
A6ARS)  FDR STUDYING AV3IDANCF  OF POLLUTANT GRADIENTS BY AQUATIC ORGANI  17- 4
ALACHLQR, AND CYCLOATE IN SEWAGE AND LAKE  WATER  /.CCMETA30LISM OF LOW   28- 1
ALBICANS FRO"1 THE NORTH SEA /.ISOLATION  OF ATY°ICAL CANDIDA             18- 4
ALTERED MICROBE /,313D5GRADATIDN IN  THE  ESTUARINE-MARINE ENVIRONMENTS    4- 1
AMOCO CADIZ OIL /fYEASTS FROM  THE  NORTH  SEA  AND                           3- 1
ANOMALOUS EFFECTS OF CONCENTRATION  ON 3IODEGRAOATION OF ORGANIC CHEMIC   3- 2
ANTIMICROBIAL ACTIVITIES Or N-CHLQ3AMINES  AND  DIAZOLIDINYL  UREA         24- 2
APPARATUS TO PRODUCE TIDAL FLUCTUATIONS  IN A SIMULATED SALT MARSH SYST  17- 3
AQUATIC ORGANISMS /,AUTOMATED  DEVICE (AGARS) FOR  STUDYING AVOIDANCE OF  17- 4
   "     MICROBIAL COMMUNITIES  /,31ODEGRADATIQN  OF  JET FUEL  BY           42- 1
   "     MICROBIAL COMMUNITIES:  AN  INTERIM REPORT  23 OCTOBER 1981 TO 3  43- i
   "     TEST SYSTEMS /.DEGRADATION  OF SELECTED  XENOBIOTIC COMPOUNDS IN  45- 2
   "     MICRQBIAL ECOLOGY /,DISCUSSION -                                 4-3
   "     MICROBIAL EC2L3GY) /.DISCUSSION:  CONCEPTS AND TRENDS C         30- 2
   "     TEST SYSTEMS /.FATE AND TOXICITY OF  HIGH  DENSITY MISSILE FUELS  44- 2
   11     ENVIRONMENT /.IMPACT OF MICRQBIAL  SEED  CULTURES IN  THE           7- 1
   11     ENVIRONMENT /.IMPACT OF THE  USE  OF MICROORGANISMS ON THE         7- 2
   11     BACTERIA /.INFLUENCE Op EASILY  DEGRADA3LS  NATURALLY OCCURRING   40- 1
   "     3ACT2RIA /.INFLUENCE OF NATURALLY  OCCURRING HUMIC ACIDS ON BIO  40- 2
   "     3ACTERIA ISOLATED eR V CONTINUOUS  CULTURE  ENRICHMENTS /.PHENYL  26- 1
        ENVIRONMENTS, PART 1
        ENVIRONMENTS. °ART 2
        ENVIRONMENTS, ?A^T 2
                             EXPOSURE  CONCENTRATION  /.USER'S  GUIDE  F  15- 1
                             FOOD CHAIN  (PROJECT  SUMMARY)  /.WASTOX.    17- 1
                             FOOD CHAIN  /,WASTOX,  A  FRAMEWORK FOR MO  16- 2
 ARENICOLA CRISTATA STIMPSON /.EFFECT  Oc  SODIUM  PENTACHLOROPHENATE ON T  37- 2
 ARENICOLIDAE) /.3EMTHIC 3IOASSAY  USING TIME-LAPSE  PHOTOGRAPHY TO MEASU  36- 2
 AROMATIC.HYDROCARBONS 3Y FUNGI /.SOME  APPROACHES  TO  STUDIES ON THE DEG  13- 2
   w     AND BRANCHED CHAIN HYDROCARBONS  BY  YEAST  /.UPTAKE  OF           19- 2
 ARTIFICIAL MICR03I4L ECOSYSTEM FOR  DETERMINING  EFFECTS AND  FATE OF TOX   3- 4
    •»      SALT-MARSH ENVIRONMENT /.EFFECTS  OF  MALATHION ON MICROORGAN   6- 1
    11      SALT-1A3SH ECOSYSTEMS — EFFECT  AMD DEGRADATION /, MICR03IAL-M   9- 1
 ATYPICAL CANDIDA ALBICANS FROM THE  NORTH  SEA /.ISOLATION OF             18- 4
 AUTOMATED DEVICE (AG4RS) FOR  STUDYING  AVOIDANCE OF POLLUTANT GRADIENTS  17- 4
                                      B
 BACTERIA ADAPTED TO LOW NUTRIENT  CONDITIONS  IN  LAKE  ONTARIO /.CHARACTE  25- 1
   "     AND FUNGI IN COASTAL SURFACE  FILMS  &S  DETERMINED 3Y A MEM8RAN  18- 3
   11     WITH MITRILOTRIACSTATE-DEGRADTNG POTENTIAL  IN AN ESTUARINE £N   5- 1
         /.EFFECT OF POLYCHLORINATED  8IPHENYL FORMULATIONS  ON THE GROW   5- 2
         /.EFFECTS OF KEPONE  ON GROWTH AND RESPIRATION OF SEVERAL ESTU  25- 2
         AND SEDIMENTARY COMMUNITIES.  PH.D. DISSERTATION.  /.FATTY ACI  20- 1
         /.INFLUENCE OF EASILY DEGRADA'-LE NATURALLY  OCCURRING CARBON S  40- 1
   "     /.INFLUENCE OF NATURALLY OCCURRING  HU«IIC 3CIDS QN  BIODEGRADAT  40- 2
   "     ISOLATED FROM CONTINUOUS CULTURE ENRICHMENTS /,PHENYLACETIC A  26- 1
 BACTERIAL AND FUMGAL OXIDATION oc OIBE^ZOFJRAN                           13- i
                                    PAGE   49
II

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                             KEYWORD  TITLE INDEX                          P    I
                                                                          A    T
                                                                          G    E
                                                                          e    M
                                      B
BACTERIAL  DEGRADATION OF DIBENZQ-P-DIOXIN AND CHLORINATED OIBENZO-P-DI   22-  1
BASS.  II.  ACCUMULATION FROM  DIETARY  SOURCES /,PCB DYNAMICS IN HUDSON R   29-  3
      MORONE  SAXATILIS.  PH.D.  DISSERTATION /, PHARMACOKINFTICS AND DIS   30-  1
BEACH,  FLORIDA 13-20 OCTOBER  1983  /.PROCEEDINGS OF THE WORKSHOP:  SIOD   11-  i
BEHAVIOR  OF  LU3WGRHS (PCLYCHAETA:  AR tIMICOLIDAE) /.BENTHIC BIOASSAY US   36-  2
BEIJERINCKIA  SPECIES /.METABOLISM  OF DIBENZQ-P-DIOXIN AND CHLORINATED    23-  1
BENTHIC 3IOASS4Y U5ING TIME-LAPSE  PHOTOGRAPHY TO MEASURE THE EFFECT OF   36-  2
   "     COMMUNITIES /,EFFECTS  OF CONTAMINATED SEDIMENTS ON REPRESENTAT   38-  1
BIOASSAY  USING TIMS-LAPSE PHOTOGRAPHY TO MEASURE THE EFFECT OF TOXICAN   36-  2
   "      ORGANISMS FOR DREDGED  MATERIAL  TESTING /.EVALUATION OF THREE    38-  2
BIOCHEMICAL  AND GENETIC PR3BES  DEVELOPED TO DETECT BIOLOGICAL CONTROL    45-  1
BIODEGRADATION 0~ DRGANIC CHEMICALS  /.ANOMALOUS EFFECTS OF CDNCENTRATI   3-  2
      "        Or SEDIMENT ASSOCIATED CHEMICALS /.ASSESSING THE          30-  4
      jl        BY MINERALIZATION O.R  CO'4ETA80LISM DETERMINED 8Y CHEMICA   47-  2
      "        IN THE tSTUARINE-MARINE ENVIRONMENTS AND THE GENETICALL   4-  1
      "        OF JET -IJEL BY  AQUATIC MICRQSIAL COMMUNITIES              42-  1
      11        OF ORGANIC CHrMICALS                                       3-  3
      "        IN FIELD AND  LABORATORY TEST SYSTEMS /.COMPARISON OF P-   42-  2
      0        PATES IM SEDIMENT/WATER CORES FROM ESTUARINE AND FRESHW   44-  1
      "        Or ORGANIC COMPOUNDS  AT LOW CONCENTRATIONS /.EFFECTS OF   39-  1
      "        0- '"1CNQSU3STITUTE,0  PHENOLS 3Y A3UATIC BACTERIA /.INFLUE   40-  1
      "        OF MO NO SUBSTITUTE!  PHENOLS 3Y AQUATIC BACTERIA /,INFLUE   40-  2
      "        KIN-TICS NAVARRE 3EACH, FLORIDA 18-20 OCTOBER 1983 /.PR   11-  1
               RAT^S 0- PESTICIDES IN WATER/SEDIMENT SYSTEMS (ABSTRACT   35-  1
BIOLOGICAL AND ABIOTIC DEGRADATION RATES 0= XEMOBIOTIC CHEMICALS IN IN   45-  3
    "      CONTR3L AGENTS IN NON-TARGET  HOSTS /.PATHOLOGIC, BIOCHEMICA   45-  1
BIOTIC AMD ABIOTIC FACTORS ACF=CTIMG SQRPTION OF TOXIC COMPOUNDS TO NA   14-  1
BIPHENYL FORMULATIONS GN THE  GROWTH  OF ESTUARINE BACTERIA /.EFFECT OF    5-  2
   "      CPC3) WITH ESTU4RINE  MICROORGANISMS AMD SHELLFISH /.EFFECTS A   14-  2
   "      TRANSPORT I'«<1 COASTAL  MARINE FQODWEBS /. POLYCHLORI.NATED          29-  1
BIPHENYLS /.INHIBITION OF ESTUARINE  MICROORGANISMS BY POLYCHLORINATEO    7-  3
    11     CPC3S) IN HUDSON RIVER STRIPED BASS, MORONE SAXATILIS.  PH.D   30-  1
BLUE  CRA3S 
-------
                            KEYWORD  TITLE  INDEX                          P    I
                                                                          A    T
                                                                          G    E
                                                                          E    M
                                      C
CHEMICALS  IN  AQUATIC ENVIRONMENTS,  PART  2:   FOOD CHAIN (PROJECT SUMMAR   17-  1
    »      IN  AJUATIC ENVIRONMENTS,  PART  2:   FOOD CHAIN /.WASTOX, A FRA   16-  2
CHEMISTRY  OF  ESTUA2INF SURFACE  MICROLAYERS  /.MICROBIOLOGY ANO            10-  1
CHLORAMINES  AND OlftZOLIDINYL  UREA  /.ANTIMICROBIAL ACTIVITIES OF H-       24-  2
CHLORDECONE)  DISTRIBUTION  IN  SEDIKENT/WATER LABORATORY SYSTEMS /,EFFEC   29-  2
CHLORINATED  DISENZO-P-OinXINS /,BACTERIAL  DEGRADATION OF DIBENZO-P-DIO   22-  1
            OI3ENZO-P-OIQXINS aY A  BEIJERINCKI4 SPECIES /.METABOLISM 0   23-  1
COASTAL  SURFACE FILMS AS DETERMINED  3Y  A MEMBRANE-ADSORPTION PROCEDURE   18-  3
   "    SURFACE SLICKS /,MIC30BIAL  POPULATIONS IN                        19-  1
   »    MARIME FDOOWSBS  /,POLYCHLORINATED  3IPH5NYL TRANSPORT IN          29-  1
COEFFICIENT  /,EFFECT CF  CONCENTRATION OF ADSORBING SOLIDS ON THE PARTI   28-  2
     "      AS THE ADSORPTION DESCRIPTOR IN EXPOSURE CONCENTRATIONS PR   16-  1
COMETABOLISM OfTE^I-NED  3Y CHEMICAL  CONCENTRATION AND ENVIRONMENT /,BI   47-  2
     "       0- L0«l CONCENTRATIONS  OP PROPACHLDR, ALACHLOR, AND CYCLOA   28-  1
     11       /.EFFECT OF SUBSTRATE  CONCENTRATION AND ORGANIC AND INORG   47-  3
COMMUNITIES  TO DEGRADATION OF XEMOBIOTIC COMPOUNDS:  EFFECTS OF CONCEN   41-  3
     «      /,BIOD=GRAOATION  CF JET  FUEL BY AQUATIC MICROBIAL            42-  1
     "        -N INTERIM REPORT 22  OCTOBER  19S1 TO 30 SEPTEMBER 1932 /   43-  1
     »'      /, EFFECTS OF CONTAMINATED SEDIMENTS ON REPRESENTATIVE ESTU   38-  1
     M        PH.D. DISSERTATION.  /.FATTY  ACID CHARACTERIZATIONS OF SE   20-  1
COMPARISON OF P-NITROPHENOL  BIOD5GRAOATION  IN FIELD AND LABORATORY TES   42-  2
COMPARISONS  OF THE PATE  OF METHYL  ^ARATHIOM IN SEDIMENT-WATER SYSTEMS    30-  3
CONCEPTS A^D TRENDS (AQUATIC  MICROBIAL ECOLOGY) /.DISCUSSION:            30-  2
CONTAMINATED HARBOR SEDIMENTS /.ACCUMULATION Oc PCS, MERCURY AND CADMI   36-  1
     "       SEDIMENT SOURCE  BY A  DEMERSAL  FISH CLtlOSTOMUS XANTHURUS)   37-  1
     "       SEDIMENTS ON  REPRESENTATIVE ESTUARINE SPECIES AND DEVELOP   38-  1
CONTAMINATION ISSUE (STATT1FNT) /.EXPLORING THE VARIOUS ASPECTS RELATE   28-  3
CONTINUOUS CULTURE ENRICHMENTS  /.PHFNYLACETIC 4CID METABOLISM BY THREE   26-  1
CORES FROM ESTUARINE AND FRESHWATER  ENVIRONMENTS /.EFFECTS Qf ADAPTATI   44-  1
CRABS CCALLINECTES SAPTDUS)  TO  STORM WATER  RUNOFF /.FIELD ANO LABORATO   23-  2
  11   TO LOW PH.  COMMENTS.  /.REACTIONS OF  BLUE                          23-  3
CRESOL AND OTHER POLLUTANTS  IN  LOTIC STREAM ECOSYSTEMS /.MICROCOSM SYS   32-  1
CRISTATA STIMPSON /,EFCECT OF SODIUM PENTACHL020PHENATE ON THE FEEDING   37-  2
CULTURE ENRICHMENTS /,PHENYLACETIC  ACID METABOLISM BY THREE AQUATIC BA   26-  1
CULTURES IM  THE AQUATIC  ENVIRONMENT  /.IMPACT OF MICRQBIAL SEED           7-  1
CURRENTS IN  SALTWATER HOLDING TANKS  /.DEVICE TO DETECT POTENTIALLY DAN   18-  1
CYCLING OF OIL IM ESTUARINc  MARSHLANDS  /.MICROBIOLOGICAL                 2-  2
CYCLOATE I'J  SEWAGE AMD LAKE  WATER  / ,CO*-1ETA30LIS M OF LOW CONCENTRATIONS   28-  1
                                      D
DANGEROUS ELECTRICAL CURRENTS IN  SALTWATER  HOLDING TANKS /.DEVICE TO D   18-  1
DEGRADABLE NATURALLY OCCURRING  CARBON SUBSTRATES ON 8IOOEGRADATION OF    40-  1
DEGRADATION  OF X5N3BIOTIC  COMPOUNDS:  EFFECTS OF CONCENTRATION, INOCUL   41-  3
     "      OF DI6ENZQ-P-DIOXIN ANO  CHLORINATED QIBENZO-P-DIQXINS /,BA   22-  1
     "      RATES OP X5NOBIOTIC CHEMICALS  IN IN VITRO ESTUARINE AND SE   45-  3
     ii      QF JPT FUEL  HYOROCARBOMS BY AQUATIC MICROSIAL COMMUNITIES:   43-  1
     11      OF M4LATHION BY  SALT-MARSH  MICROORGANISMS                    4-  2
     "      QF s-L-CTED  XEN03IOTIC  COMPOUNDS IN THREE TYPES OF AQUATIC   45-  2
            IN ESTUARINE A.MD  FRESHWATER SITES /. QI3UTYLPHTHALATE         46-  2
     "      OF 14C-K=?ON>  IN  ESTUARINE  MICROCOSMS /.FATE AND             21-  1
     "      OF XENOBIOTIC  COMPOUNDS  /,MICRQBIAL                          8-  3
     "      OF HAL3G-NAT-D HYDROCARBONS /.MICROBIAL                      8-  2
     11      /.'-1ICROBIAL-MALATHION  INTERACTION IN ARTIFICIAL SALT-MARSH   9-  1
     "      OF AROMATIC  HYDROCARBONS BY FUNGI /.SOME APPROACHES TO STU   13-  2
     «      OF POLLUTANTS  IN  MARINE  ENVIRONMENTS /.WORKSHOP:  MICROBIA   11-  3
DEGRADING POTENTIAL IN AN  ESTUARINE  ENVIRONMENT /.DISTRIBUTION OF 8ACT   5-  1
DEMERSAL FISH 
-------
                            KEYWORD  TITLE  INDEX                          P   i
                                                                         A   T
                                                                         G   E
                                                                         E   M
                                      D
DESIGN  FACTORS AFFECTING ENVIRONMENTAL  FATE  STUDIES  IN MICROCOSMS /,SY  34- 1
DETECT  POTENTIALLY DANGEROUS ELECTRICAL CURRENTS  IN  SALTWATER HOLDING   18- 1
  "     BIOLOGICAL CONTROL AGENTS  IN  NCM-TARGET  HOSTS /.PATHOLOGIC, BIO  45- 1
DETERMINED ti Y CHEMICAL CONCENTRATION AND ENVIRONMENT /,BIQDEGRADATION   47- 2
           BY A MEMBRANE-ADSORPTION  PROCEDURE  /.DENSITIES  OF BACTERIA   18- 3
DETERMINING EFFECTS AND PATE 0^ TOXICANTS  IN A  SALT-MARSH  ENVIRONMENT    3- 4
DEVELOPED TO DETECT 3I3LOGICAL CONTROL  AGENTS  IN  NON-TARGET HOSTS /,PA  45- 1
DEVELOPING BSNTHIC COMMUNITIES /.EFFECTS OF  CONTAMINATED SEDIMFNTS ON   38- 1
DEVELOPMENT GF A FATE/TOXICITY SCREENING TEST                            46- 1
DEVELOPMENTS IN INDUSTRIAL MICROBIOLOGY, VOL.  15                         27- 2
DEVICE  CAGARS) FOR STUDYING AVOIDANCE  OF POLLUTANT GRADIENTS BY AQUATI  17- 4
       TO DETECT POTENTIALLY DANGEROUS  ELECTRICAL CURRENTS IN SALTWATE  18- 1
DIAZOLIDINYL UREA /.ANTIMICROBIAL ACTIVITIES OF N-CHLORAMINES AND       24- 2
DIBENZO-P-DIOXINS /.BACTERIAL DEGRADATION  OF DIBENZO-P-DIOXIN AND CHLO  22- 1
   "    P-3IOXIN AMD CHLORINATED  DIBENZO-P-DIOXINS /,BACTERIAL DEGRAQA  22- 1
   11    (1,4>DIOXAN 3Y A PSEUOOMONAS SPECIES /.METABOLISM  OF            22- 2
   "    P-DIOXIN AMD CHLORINATED  DIBENZO-P-DIOXINS BY  A  BEIJERINCKIA S  23- 1
   "    P-OIQXINS 3Y A BEIJERINCKIA  SPECIES  /,METABOLISM OF DIBENZO-P-  23- 1
DIBENZOFURAN /,BACTERIAL AND FUNGAL  OXIDATION  OF                         13- 1
DIBUTYLPHTHALATE DEGRADATION IN -STUARINE  AND  FRESHWATER SITES          46- 2
DIETARY ACCUMULATION 0= PC8S FROM A  CONTAMINATED  SEDIMENT  SOURCE BY A   37- 1
   "    SOURCES /,PC3 DYNAMICS IN HUDSON RIVER  STRIPED 8ASS. II, ACCUM  29- 3
   11    POLYCHL03IMATED 3IPHENYLS CPCBS) IN  HUDSON RIVER STRIPED BASS,  30- 1
DIQXAN  BY A PSEUDQMONAS SPECIES /,METABOLISM OF DI8ENZO  (1,4)           22- 2
DIOXIN  AND CHLORINATED DIBENZO-P-DIOXINS /»BACTERIAL DEGRADATION OF 01  22- 1
  11    AND CHLORINATED D IBtN ZO-P-DIOXI MS BY  A  BEIJERINCKIA SPECIES /»M  23- 1
DIOXINS /,3ACT£RIAL DEGRADATION OF DIBENZO-P-DIOXIM  AND  CHLORINATED 01  22- 1
   "    3Y A BcIJERINCXIA SPECIES /.METABOLISM  OF DIBENZO-P-DIQXIN AND  23- 1
DISSERTATION, /,FATTY ACID CHARACTERIZATIONS OF SELECTED SULFATE-REDUC  20- 1
     "        /,PHARMACQKINSTICS AND  DISTRIBUTION  OF  DIETARY POLYCHLORI  30- 1
DISSOLVED ORGANIC CARBON AND SECOND  SUBSTRATES  ON THE  BIODEGRADATION 0  39- 1
DISTRIBUTION 0? 3ACT5RIA WITH NITRILOTRIACcTATS-DcGRADING  POTENTIAL IN   5- 1
     "        IN SEDIMENT/WATER LABORATORY  SYSTEMS /,EFFECTS OF LUGWORM  29- 2
     «        OF DIETARY PQLYCHLORINATEO 3IPHSNYLS (PCBS) IN HUDSON RIV  30- 1
DREDGED MATERIAL TESTING /»E VALU4TIO'-)  OF THREE  FISH  SPECIES AS BIOASSA  38- 2
   "    SPOIL MATERIAL IN THE OCCAM  AND THE  PCS CONTAMINATION ISSUE CS  28- 3
DUMPING OF DREDGED SPOIL MATERIAL IN THE OCEAN  AND THE PCB CONTAMINATI  28- 3
DYNAMICS OF MI?EX AND ITS PRINCIPAL  PHDTOPROOUCTS IN A SIMULATED MARSH  18- 2
   "     IN HUDSON RIVER STRIPED  BASS.  II. ACCUMULATION  FROM DIETARY S  29- 3
                                      E
EASILY  D5GRADA3L5 NATURALLY OCCURRING  CARBON SUBSTRATES  ON 8IODEGRADAT  40- 1
ECOLOGY /.DISCUSSION - A3UATIC MICR03JAL                                 4- 3
   "     /.DISCUSSION:  CONCEPTS  AND TRENDS  CAQUATIC MICROBIAL          30- 2
ECOSYSTEM FOR DETERMINING EFFECTS AND  FATE OF  TOXICANTS  IN A SALT-MARS   3- 4
ECOSYSTEMS—EFFECT AND DEGRADATION /,MICR03IAL-MALATHION INTERACTION I   9-1
           /.MICROCOSM SYSTEM TO  MODEL  THE FATE AND  EFFECTS OF P-CRESO  32- 1
    "      /.MODEL                                                       32" 2
EFFLUENTS /.AVOIDANCE RESPONSES OF ESTUARINE ORGANISMS TO  STORM WATER   24- 1
ELECTRICAL CURRENTS IN SALTWATER  HOLDING TANKS  /.DEVICE  TO DETECT POTE  18- 1
ENRICHMENTS /, PH'-NYL ACETIC ACID METABOLISM BY  THREE  AQUATIC BACTERIA I  26- 1
ENVIRONMENT /.ARTIFICIAL MICR03IAL ECOSYSTEM FOR  DETERMINING EFFECTS A   3-4
     "       /jSIODEGRADATIQN BY MINERALIZATION  OR COMETASOLISM DETERMI  47- 2
     "       /•DISTRIBUTION OF BACTERIA  WITH  NITRILOTRIACETATE-DEGRADIN   5- 1
     "       /,CFFECTS OF MALATHION ON  MICROORGANISMS OF  AN ARTIFICIAL    6- 1
     "       /.IMPACT OF MICR08IAL SEED  CULTURES IN THE AQUATIC           7- 1
     "       /.IMPACT OF THE USE OF MICROORGANISMS ON THE AQUATIC         7- 2
     »       /.INTERDEPENDENT MICROCOSMS FOR  THE ASSESSMENT Oc POLLUTAN   8- 1
ENVIRONMENTAL POLLUTANTS /.FATE AND  EFFECTS  3F  POLLUTANTS:  FATE QP     30-  5
                                   PAGE  52

-------
                            KEYWORD  TITLE  INDEX
ENVIRONMENTAL
      w
             =ATE
             CATE
                   AND FFF'ECTS ASSESSMENTS  /.PERSPECTIVE  OM  THE  ROLE 0
                   STUDIES IN MICROCOSMS  /,SYSTEM  DESIGN  FACTORS AFFEC
ENVIRONMENTS  AND_THE GENETICALLY ALTERED  MICROBE /,BIQTEGRADATION IN T
     "        /.E.-FECTS OF ADAPTATION  DM BIOOEGSAOATIQN  RATES IN  SEDIME
     "          RESULTS F?OM A -IELD APPLICATION  (ABSTRACT) /,FATE DF F
                       EXPOSURE CONCENTRATION  /.USER'S  GUIDE FDR WASTO
     n
     n
             PART
             PART
             2 ART
l:
2'.
2:
                       FOOD
FOOD
                            CHAIN
                            CHAIN
    u
    n
                                  (PROJECT SUGARY) /.a'ASTDX,  A FRAMEW
                                  /t^ASTQXf A FRAMEWORK FOR MODELING  T
             /.WDRKSHOP:  MICROBIAL DEGRADATION DF POLLUTANTS  IN MARIN
ESTUARINE  ORGANISMS TO STORM WATER RUNOFF AND PULP MILL EFFLUENTS  /,AV
    «'      MARINE ENVIRDNMENTS AND THE GENETICALLY ALTERED MICROBE  /,8I
    «      AND S-OI^IENT/WATER SYSTEMS /.BIOLOGICAL AND ABIOTIC  OEGRADAT
    "      AND FRESHWATER SITES /,DIBUTYLPHTHALATE DEGRADATION  IN
    "      ENVIRONMENT /.'DISTRIBUTION OF SACTERIA WITH NITRILOTRIACET AT
    11      '5ACTERIA /.EFFECT DF P OLYCHLORINATED BIPHENYL FORMULATIONS  0
    H      MICROORGANISMS AND SHELLFISH /.EFFECTS AND INTERACTIONS  OF  P
    "      AND FRESHWATER ENVIRONMENTS /.EFFECTS OF ADAPTATION  ON BIODE
    "      SPECIES AND DEVELOPING BcNTHIC COMMUNITIES /»EFFECTS OF  CONT
    »      MICROORGANISMS /.EFFECTS OF KEPCNE ON
    "      BACTERIA /.EFFECTS OF KEPQNE ON GROWTH AND RESPIRATION OF SE
          SURFACE -ILMS /,EFFECTS DF POLLUTANTS ON MICR03IAL ACTIVITIE
          MICROBES AND ORGANOCHLORINE PESTICIDES (A SRIEF REVIEW)
    "      MICROCOSMS /,FATE AND DEGRADATION OF 14C-KEPONE IN
    "      SITES /.FATE OF METHYL PARATHION IN WATER AND SEDIMENT TEST
    "      MICROORGANISMS BY POLYCHLO^INATEO BIPHENYLS /.INHIBITION OP
    "      SURFACE SLICKS /.MICR03IAL INTERACTIONS WITH PESTICIDES  IN
    "      MARSHLANDS /,MICRO3IOLDGICAL CYCLING OF OIL IN
    "      SURFACE MICRDLAYERS /.MICROBIOLOGY AND CHEMISTRY OF
    "      MICRDCOS-1S PERTURBED BY CARBARYL, METHYL PARATHION AND
EXTRAPOLATION /.SYNOPSIS OF DISCUSSIDN SESSION:
                                     F
     ASSESSMENTS; COMPARISONS OF THE FATE DF METHYL PARATHION  IN
     OF METHVL PARATHION IN SEDIMENT-WATER SYSTEMS /.APPLICATION
     OF TOXICANTS IN A SALT-MARSH ENVIRONMENT /.ARTIFICIAL MICROBIAL  E
     TOXICITY SCREENING TEST /,DEV5LQPMENT OF 4
     AND DEGRADATION OF 14C-KEPONE IN ESTUARINE MICROCOSMS
     OF ENVIRONMENTAL POLLUTANTS /.FATE AND EFFECTS OF POLLUTANTS:
     AND EFFECTS OF POLLUTANTS:  FATE DF ENVIRONMENTAL POLLUTANTS
     AND TOXICITY DF HIGH DENSITY MISSILE ^UELS RJ-5 AMD JP-9  IN AQUAT
     OF FENTHIDN IN SALT MARSH ENVIRON'IE.NTS:  RESULTS FROM A FIELD APP
     OF METHYL PARATHIDN IN WATER AND SEDIMENT TEST SYSTEMS FROM FRESH
     AND EFFECTS Or P-CRESOL AND OTHER POLLUTANTS IN LOTIC STREAM  SCOS
     AND EFFECTS ASSESSMENTS /.PERSPECTIVE ON THE ROLE OF MICROCOSMS  I
FATE
                                                                  PENTA
                                                                  SEDIM
                                                                  OF MI
  "
  "
 n
 u
 n
                           /,SYSTEM DESIGN FACTORS
     STUDIES IN MICROCOSMS
     OF TGXIC CHEMICALS IN AQUATIC  ENVIRONMENTS,  PART
     OF TOXIC CHEMICALS IN AQUATIC  ENVIRONMENTS,  PART
 "   OF TOXIC CHEMICALS IN AQUATIC  ENVIRONMENTS,  PART  I:
 FATTY ACID CHARACTERIZATIONS OF  SELECTED  S'JLFATE-REDUC ING
                                 AFFECTING ENVIRONME
                                    I:   EXPOSURE CON
                                    2",   FOOD CHAIN C
                                    2:   CDOD CHAIN /
                                        '.ACTERIA AND
 FEEDING BEHAVIOR OF LUSH3RMS  CPOLYCHAETA:   ARENICOLlDAE) /.BENTHIC BIO
   11    ACTIVITY 0- THE LUGWOR'1,  ARENICOLA  CRISTATA  STIMPSON /,EFFECT
 FENTHIQN IM SALT MARSH ENVIRONMENTS:   RESULTS  =ROM A  FIELD APPLICATION
 FIELD AND LABORATORY TEST  SYSTEMS  /,COMPARISON OF  P-NITROPHENOL  BIODEG
  "   APPLICATION CA3STRACT)  /,FAT=  OF FENTHIQM IN SALT MARSH iNVIRONM
  "   AND LABORATORY AVOIDANCE  REACTIONS  BY 3LUE CRA3S CCALLINECTES SA
 FISH (LEIOSTOMUS X4NTHURUS) /.DIETARY  ACCUMULATION OF °CBS FROM  A CONT
 "   SPECIFS AS 5IDASSAY ORGANISMS  FOR DREDGED MATERIAL TESTING  /,EVAL
 FLORIDA 13-20 .JCTOUES 19^3 /,PROCEEDINGS  o^= THE WORKSHOP:  SIODEGRADAT
 FLUCTUATIONS.iN A SIMULATED SALT  HARSH SYSTEM  /,APPARATUS TO PRODUCE T
                                    PAGE  53
P   I
A   T
G   E
£   M

33- 1
34- 1
 4- 1
44- 1
27- 1
15- 1
17- 1
16- 2
11- 3
24- 1
 4- 1
45- 3
46- 2
 5- 1
 5- 2
14- 2
44- 1
38- 1
 5- 3
25- 2
 1- 2
 6- 2
21- 1
31- 1
 7- 3
 2- 1
 2- 2
10- 1
17- 2
33- 2

30- 3
30- 3
 3- 4
46- 1
21- 1
30- 5
30- 5
44- 2
27- 1
31- 1
32- 1
33- 1
34-1
15- 1
17- 1
16- 2
20- 1
36- 2
37- 2
27- 1
42- 2
27- 1
23- 2
37- 1
38- 2
11- 1
17- 3

-------
                             KEMvORQ TITLE INDEX                          P   I
                                                                          A   T
                                                                          G   £
                                                                          S   M

FOOD  CHAIN (PROJECT  SUMMARY) /,W4STOX, A FRAMEWORK FOR  MODELING  TH? FA  17- 1
 «    MAIN /.WASTOX, A  FRAMEWCSK FIR MODELING THE FATE  OF  TOXIC  CHEMIC  16- 2
^XSSL'l™^0"1-™11"1*0  BIPHE-YL TRANSPORT IN COASTAL MARINE          29- 1
FRAMEWORK rOR MoO=:LI,MG  THE  FATE OF TOXIC CHEMICALS IN  AQUATIC  ENVIRONM  15- 1
    "     .-3R MODELING  THE  FATE OF TOXIC CHEMICALS IN  AQUATIC  ENVIRONM  17- 1
          f=0» MODELING  THr  FATE OF TOXIC CHEMICALS IN  AQUATIC  ENVIRONM  16- 2
FRESHWATER SITES /.DIBUTYLPHTHALATE DEGRADATION IN ESTUARIN5 AND        46- 2
    11      ENVIRONMENTS /,EFFECTS OF ADAPTATION ON BIODEGRAQATION  RATE  44- 1
           AND F.STJARINE SIT^S /,FATE OF METHYL PARATHIQN  IN WATER AND  31- 1
FUEL BY AC'JATIC MTCROBIAL COMMUNITIES /, 3IHDEGR ADATION  0-  JET            42- 1
 «    HYDROCARBONS  5Y AQUATIC HICR03IAL COMMUNITIES:  AN INTERIM  REPORT  43- 1
FUELS RJ-5 AND JP-9  IN  AQUATIC TEST SYSTEMS /.FATE AND  TOXICITY  OF HIG  44- 2
FUNGAL OXIDATION OF  OI3ENZ3FURAN /.BACTERIAL AMD                         13- 1
FUNGI IN COASTAL SURFACE FILMS AS DETERMINED BY A MEMBRANE-ADSORPTION   18- 3
  11   /,,;FCECT o=  HEPTAC-HLJR ON MEXAOECANE UTILIZATION  BY  SELECTED      41- i
  «   /.SOME APPROACHES TO  STUDIES ON THE DEGRADATION  OF AROMATIC  HYDR  13- 2
                                      G
GENETIC PROBES DEVELOPED TO DETECT BIOLOGICAL CONTROL  AGENTS IN  NON-TA  45- 1
GENETICALLY ALTERED  MICROBE /,BIODEGRAQATIQN IN THE ESTUARINE-MARINE £   4-1
GRADIENTS 3Y AQUATIC ORGANISMS /»AUTOMATED DEVICE (AGARS)  ^OR  STUDYING  17- 4
GROWTH 0- ESTUARINE  3ACTERIA /,EFFECT OF POLYCHLGRINATcD 8IPHENYL  FORM   5- 2
  11    AND RESPIRATION  Or SEVERAL ESTUARINE 3ACTERIA /,EFFECTS OF  KEPO  25- 2
GUIDE FOR WASTOX,  4  FRAMEWORK FOR MODELING THE FATE OF  TOXIC CHEMICALS  15- 1
                                      H
HALOGENATED HYOR3CUR80NS /»MICRQ3IAL DEGRADATION OF                       8~ 2
HARBOR SEDIMENTS /,ACCUMULATION OF PCS, MERCURY AND CADMIUM BY NEREIS   36- 1
HEPTACHLOR ON HEXAOECAME UTILIZATION SY SELECTED FUNGI  /,EFFECT  OF      41- 1
HEXADECANE UTILIZATION  BY SELECTED FUNGI /,EFFECT OF HEPTACHLQR  ON      41- 1
HOLDING TANKS /,DEVICE  TO DETECT POTENTIALLY DANGEROUS  ELECTRICAL  CURR  18- 1
HOSTS /.PATHOLOGIC,  BIOCHEMICAL AND GENETIC PROBES DEVELOPED TO  DETECT  45- 1
HUDSON RIVER STRIPED EASS,  II. ACCUMULATION FROM DIETARY SOURCES /,PCB  29- 3
  "    RIVER STRIPED BASS,  MORQNE SAXArjLIS.  PH.D, DISSERTATION /,PHA  30- 1
HUMIC ACIDS ON 2IODEGRADATION OF MONQSUBSTITUTED PHENOLS BY AQUATIC BA  40- 2
HYDROCARBONS BY AQUATIC MICROBIAL COMMUNITIES:  AN INTERIM REPORT  23 0  43- 1
     n       /,f«IC?>03IAL DEGRADATION Or HALOGFNATEO                       8- 2
     «       BY PU-JGI /,SOME APPROACHES TO STUOIES ON  THE  DEGRADATION   13- 2
     «       BY YEAST /.UPTAKE OF AROMATIC AND BRANCHED CHAIN            19- 2
                                      I
IMPACT Q* MICROBIAL  SESD CULTURES IN THE AQUATIC ENVIRONMENT              7- 1
  11    OF THE USE  OF MICROORGANISMS ON THE AQUATIC ENVIRONMENT           7- 2
INDUSTRIAL MICR03IOLOGV, VOL. 15 /.DEVELOPMENTS IN                       27- 2
    "      YEASTS  =03 OATHOGENICITY /.EVALUATION OF                      21- 2
INHIBITION OF ESTUARINE MICROORGANISMS 3Y POLYCHLORINATED  3IPHENYLS      7- 3
INOCULUM, SNO CHEMICAL  STRUCTURE /,ADAPTATION OF NATURAL MICROSIAL COM  41- 3
INORGANIC COMPOUNDS  ON  THE  OCCURRENCE AND RATE OF MINERALIZATION AND C  47- 3
INSECTICIDE PFRSISTE^iCn IN  NATURAL SSAWATER AS AFFECTED BY SALINITY, T  47- 1
INTERACTION IN ARTIFICIAL SALT-MARSH ECOSYSTEMS—EFFECT 4ND DEGRADATIO   9- 1
INTERACTIONS OF PQLYCHLORINATE!? BI?H = NYL CPCB) WITH ESTUARINE  MICROORG  14- 2
     «       WITH  PESTICIDES IN ESTUftRINS SURFACE SLICKS /,MICROBIAL     2- 1
     «       8cTWE=N POLLUTANTS AND MICROORGANISMS /fUSE OF MICROCOSMS  34- 2
INTERDEPENDENT MICROCOSMS FOR THS ASSESSMENT OP POLLUTANTS IN  THE  MARI   8- 1
INTERFACE IN LABORATORY SYSTEMS /.MOVEMENT Oc KEPONE ACROSS AN UNDISTU  32- 3
INTERIM REPORT 23  OCTOBER 1981 TO 30 SEPTEMBER 1982 /.DEGRADATION  OF J  43- 1
                                      J
JET FUEL SY AQUATIC  MICROBIAL COMMUNITIES /,3IODSGRAOATION OF            42- 1
 "   FU-L HYDROCARBONS BY AQUATIC MICR03IAL COMMUNITIES:  AN INTERIM RE  43- 1
JP-9 IN AQUATIC TEST SYSTEMS /,FATE 4ND TOXICITY 0^ HIGH DENSITY MISSI  44- 2
                                      K
KEPQNE ON ZSTU^RIN'E  MICROORGANISMS /.EFFECTS OF                           5- 3
                                    PAGE  54

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                            KEYWORD  TITLE  INDEX                          P    I
                                                                         A    T
                                                                         G    e
                                                                         E    M
                                      K
REPONE  ON  GROWTH AMD RESPIRATION Or  SEVERAL  ESTUARINE 3ACT-RIA /.EFFEC  25-  2
       (CHLORDECONE) DISTRIBUTION  IN  SEDIMENT/rfATER  LABORATORY SYSTEMS  29-  2
       IN  ESTUARINS MICROCOSMS /.FATE AND  DEGRADATION OF 14C-           21-  1
  «     ACROSS AN UNDISTURBED  S?D IMENT-WATES  INTERFACE IN LABORATORY SY  32-  3
  »     AND METHYL »ARATHIQ?J /,VALIDITY  Or  °ARTITIQM  CO-FFICICNT AS THE  16-  1
KINETICS  NAVARRE BEACH, FLORIDA  18-20 OCTOBER  1983  /.PROCEEDINGS OF TH  11-  1
                                      L
LAKE  ONTARIO /.CHARACTERISTICS Or  BACTERIA ADAPTED  TO LOW NUTRIENT CON  25-  1
 »   WATER /,CQMETAB3LISM OF  LOW CONCENTRATIONS  OF  PRO^ACHLOR, ALACHLO  28-  1
LAPSE PHOTOGRAPHY TO MEASURE  THE EFFECT OF TOXICANTS ON THE FEEDING SE  36-  2
LEIOSTOMUS XANTHURUS) /.DIETARY  ACCUMULATION OF  PCBS FROM A CONTAMINAT  37-  1
LIPOLYTICA /.PURIFICATION AND CHARACTERIZATION OF  A  NEUTRAL PROTEASE F   1-1
LOTIC STREAM ECOSYSTEMS /.MICROCOSM  SYSTEM TO  MODEL  THE FATE AND EFFEC  32-  1
LOW  NUTRIENT CONDITIONS IN LAKE  ONTARIO /.CHARACTERISTICS 3F BACTERIA   25-  1
 "  CG,NC£NTRATIO;4S 0= PROPACHL3R,  ALACHLOR,  AND  CYCLOATE IN SEWAGE AND  28-  1
 «  CONCENTRATIONS /.EFFECTS  OF  DISSOLVED  ORGANIC  CARBON AND SECOND SU  39-  1
 »  PH.  COMMENTS. /.REACTIONS OF  BLUE  CRASS TO                          23-  3
LU6WORM,  ARENICOLA CRISTATA STIMPSON  /,EFFECT  OF SODIUM PENTACHLOROPHE  37-  2
LUGWORMS  C°QLYCHAETA:  ARENICOLIDAE)  /.BENTHIC BIQASSAY USING TIME-LAP  36-  2
   "      AMD SrAGRASS ON KtPONt  CCHLQR9ECOME)  DISTRIBUTION IN SEDIMENT  29-  2
                                      M
MALATHION 3Y SALT-MARSH MICROORGANISMS  /.DEGRADATION OF                  4-  2
    "     3M MICROORGANISMS OF AN  ARTIFICIAL SALT-MARSH ENVIRONMENT /»   6-  1
    "     INTERACTION IN ARTIFICIAL  SALT-MARSH ECOSYSTEMS—EFFECT AND    9-  1
MARINE ENVIRONMENTS AND THE GENETICALLY ALTERED  MICROBE /,BIODEGRAOATI   4-  1
  «     ENVIRONMENT /,INTSRDEPE^QENT  MICROCOSMS FOR  THE ASSESSMENT OF P   8-  1
  "     F303WE63 /.PCLYCHLOSINATED  tJlPHSNYL TRANSPORT IN COASTAL         29-  1
  "     ENVIRONMENTS /,WORKSHOP:  MICR03IAL DEGRADATION OF POLLUTANTS I  11-  3
MARSH SYSTEM /.APPARATUS TO PRODUCE  TIDAL  FLUCTUATIONS IN A SIMULATED   17-  3
  "    ENVIRONMENT /.ARTIFICIAL MICR08IAL ECOSYSTEM  FOR DETERMINING EFF   3-  4
  "    MICROORGANISMS /.DEGRADATION  Or MALATHIOM  BY  SALT-                 4-  2
  "    SYSTEM /.DYNAMICS OF MIREX AND  ITS PRINCIPAL  PHOTOPRQDUCTS IN A   18-  2
  *>    ENVIRONMENT /.rFFECTS OF MALATHION ON  MICROORGANISMS OF AN ARTIF   6-  1
  "    ENVIRONMENTS:  RESULTS  FROM  A  FIELD  APPLICATION (ABSTRACT) /.FAT  27-  1
  "    ECOSYSTEMS—EFFECT AND  DEGRADATION /,MIC3Q8IAL-MALATHION INTERAC   9-  1
MARSHLANDS /,MIC^OEIOL3GICAL  CYCLING  OF OIL  IN ESTUARINE                 2-  2
MEMBRANE-ADSORPTION PROCEDURE /.DENSITIES  OF BACTERIA AND FUNGI IN COA  18-  3
MERCENARIA MERCENARIA AND PALAEM3N"TrS  PUGIO FROM  CONTAMINATED HARBOR   36-  1
    «      AND FALAEMONETES PUGIO  FROM  CONTAMI?JATED  HARBOR SEDIMENTS /  36-  1
MERCURY AND CADMIUM 3Y NEREIS VISE.MS, MERCENARIA MERCENARIA AND PALAEM  36-  1
METABOLISM OF 9I1ENZQ C1.4)DIOXAN  BY  A  PSEUDQMQNAS  SPECIES              22-  2
    "      OF DI3ENZJ-P-OIOXIN AMD  CHLORINATED OIBENZO-P-DIOXINS BY A   23-  1
    "      BY TH^ES AQUATIC 3ACT5RIA  ISOLATED  -ROM  CONTINUOUS CULTURE   26-  1
METHYL PARATHI1N IN SEDIMENT-WATER  SYSTEMS /.APPLICATION OF MICROCOSM   30-  3
  "     PARATrilON IN WATER AND SEDIMENT  TEST  SY5TEMS  FROM FRESHWATER AN  31-  1
  11     PARATHION AND PENTACHLOROPHENOL  /,SUCCESSION  OF MICROFUNGI IN E  17-  2
  "     PARATHION /.VALIDITY OF PARTITION COEFFICIENT AS THE ADSORPTION  16-  1
MICROBE /,3iaDcGRA3ATION IN THE  SSTUARINE-MA^I^E ENVIRONMENTS AND THE    4-  1
MICROBES  A'JD 03GAN3CHL3RINE PESTICIDES  CA  3RIEF  REVIEW) /,ESTUARINE      6-  2
HICROBIAL COMMUNITIES TO DEGRADATION  OF XEN03IQTIC  COMPOUNDS:  EFFECTS  41-  3
    "     -CDSYSTFM FO? DETERMINING  EFFECTS  AND  FATE OF TOXICANTS IN A   3-4
    "     COMMUNITIES /,3I3DtGRAOATION  OF  JET  FUEL  BY AQUATIC           42-  1
    11     COMMUNITIES:  AN INTERIM  REPORT  23 OCTOBER 1981 TO 30 SEPTEM  43-  i
    "     ECOLOGY /.DISCUSSION - AQUATIC                                 4-  3
    "     ECOLOGY) /^DISCUSSION:   CONCEPTS AND TRENDS (AQUATIC          30-  2
    "     ACTIVITIES IN ESTUARINE  SURFACE  FILMS  /.EFFECTS OF POLLUTANT   1-  2
          SEED CULTURES IN THE AQUATIC  ENVIRONMENT  /.IMPACT OF           7-  1
                      OF XtNDBIOTlC  COMPOUNDS                             8-  3
                                    PAGE  F5

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M

H
                         KEYWORD TITLE INDEX
                                      M
MICROBIAL  DEGRADATION OF HALDGrNATcO HYDROCARBONS
          INTERACTIONS WITH  PESTICIDES IN ESTUARINE SURFACE SLICKS
          POPULATIONS IN COASTAL  SURFACE SLICKS
          FOXICITY STUDIES
    "      MALATHIOM INTERACTION  IN  ARTIFICIAL SALT-MARSH ECOSYSTEMS--E
    "      DEGRADATION OF POLLUTANTS IN MARINE ENVIRONMENTS /.WORKSHOP:
MICROBIOLOGICAL CYCLING IF OIL  I'
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II

It     CI
                            KEYWORD  TITLE  INDEX                         P    I
                                                                         A    T
                                                                         G    E
                                                                         E    M
                                      0
ORGANIC  CHEMICALS / , 31CJOEGR.AOATION  0-                                    3-  3
        ANO INORGANIC COMPOUNDS  ON  THE  OCCURRENCE AND RATE OF MINERALI  47-  3
        CARBON A.-^C SECOND SUBSTRATES ON THS 8I3DEGRAOATIflN OF ORGANIC   39-  1
   "     COMPOUNDS AT LOW CONCENTRATIONS /,EFFECTS OF DISSOLVED ORGANIC  39-  1
ORGANISMS /, AUTOMATED DEVICE  CAG.1RS) FOP STUDYING AV2IDANC= OF POLLUTA  17-  4
          TO STORM WATER RUNCFF  ANO  PULP MILL =FCLJENTS /.AVOIDANCE RE  24-  1
           •OR DREDGED MATERIAL TESTING  /.EVALUATION OF THREE FISH SPEC  38-  2
ORGANOCHLORINE PESTICIDES (A  BRIEF  REVIEW)  /.ESTUARINE MICROBES AND      6-  2
OXIDATION DF DIE ENZOFUSAN /.BACTERIAL AND  FUNGAL                        13-  1
                                      P
P-DIOXIN AND CHLORINATED DIBENIO-P-DIQXINS  /iBACTERIAL DEGRADATION OF   22-  I
 -DIOXINS /, BACTERIAL OEGRADATIOM  OF DIBENZO-P-DIOXIN AND CHLORINATED   22-  1
 -MITROPHEMOL 3I3DEGRAOATIJN  IN  FIELD ANO  LABORATORY TEST SYSTEMS /.CO  42-  2
 -DIOXIN AMD CHLORINATED DI6ENZO-P-DIOXINS  BY A 8EIJERINCKIA SPECIES /  23-  1
 -DIOXINS 3Y A 8EIJERIMCKIA  SPECIES  /.META30LISM OF DI3ENZO-P-DIOXIN A  23-  1
 -CRESGL A^D OTHER POLLUTANTS IN LQTIC  STREAM ECOSYSTEMS /.MICROCOSM S  32-  1
PALAEMONETES PUGIO F^OM CONTAMINATED HARBOR SEDIMENTS /.ACCUMULATION 0  36-  1
PARATHION IN SEDIM5NT-WAT£R  SYSTEMS  /.APPLICATION OF MICROCOSM STUDIES  30-  3
    "     IN WATER AMD SEDIMENT  TEST SYSTEMS FROM FRESHWATER AND ESTUA  31-  1
    "     AND PENTACHLORQPHEMOL  /.SUCCESSION OF MICRQFUNGI IN ESTUARIN  17-  2
    "     /.VALIDITY Cr PARTITION  COEFFICIENT AS THE ADSORPTION OESCRI  16-  1
PART l:   EXPOSURE CONCENTRATION  /.USER'S GUIDE FOR W4STCX, A FRAMEWORK  15-  1
 11   2:   FOOD CHAIN CP20JECT  SUMMARY) /.WASTQX, ft FRAMEWORK FOR MOOELI  17-  1
 11   2:   FOOD CHAIM /, WASTQX, A  PRAM£WQRK  FOR MODELING THE FATS OF TOX  16-  2
PATHOGENICITY /.EVALUATION OF INDUSTRIAL YEASTS FOR                     21-  2
PATHOLOGIC, BIOCHEMICAL AND  GENETIC  PROBES  DEVELOPED TO DETECT 8IOLOGI  45-  1
PCS, M'rRCURY AND CADMIUM BY  NEREIS  VIRENS.  McRCENARIA MERCENARIA AND P  36-  1
 "   WITH 5STUARIM5 MICROORGANISMS  AND  SHELLFISH /.EFFECTS AND INTERAC  14-  2
 "  CONTAMINATION ISSUE (STATEMENT)  /.EXPLORING THE VARIOUS ASPECTS RE  28-  3
 "  DYNAMICS IN HUDSON RIVER  STRIPED BASS.  II. ACCUMULATION FROM DIETA  29-  3
PCBS FROM A CONTAMINATED ScDIMENT  SOURCE BY A DEMERSAL FISH (LEIOSTOMU  37-  1
 11    IN HUDSON RIVER STRIPED BASS,  MORONE  SAXATILIS,  PH.D. DISSERTAT  30-  1
PENTACHLQROPHENATE C'J THE FEEDING  ACTIVITY  OF THE LUGWORM, ARENICOLA C  37-  2
PENTACHLOROPHENOL /.SUCCESSION 0^  MICROFUNGI IM 5STUARINE MICROCOSMS P  17-  2
PERSISTENCE IN NATURAL SEAWATER  AS  AFFECTED BY SALINITY, TEMPERATURE,   47-  1
PERSPECTIVE ON THE ROLE OF MICROCOSMS IN ENVIRONMENTAL FATE AND EFFECT  33-  1
PERTURBED 3Y CARBA9YL, METHYL PARATHION AND PE-MTACHLOROPHENOL /.SUCCES  17-  2
PESTICIDES (A 3RI£^ REVIEW)  /.ESTUARIN-E MICROBES AND OSGANOCHLORINE      6-  2
    "      IN tSTUARINS SURFACE  SLICKS  /.MICR03IAL INTERACTIONS WITH     2-  1
    11      IN WATE^/SEOIMENT  SYSTEMS (ABSTRACT) /.VARIABILITY OF BIODE  35-  1
PHARMACOKINETICS A'JD DISTRIBUTION  OF DIETARY POLYCHLQRINATED BIPHENYLS  30-  1
PHENOLS  3Y AQUATIC BACTERIA  /.INFLUENCE OF  EASILY OEGRADABLE NATURALLY  40-  1
   "    3Y AQUATIC BACTERIA  /.INFLUENCE OF  NATURALLY OCCURRING HUMIC A  40-  2
PHENYLACETIC ACID METABOLISM  BY  THREE AQUATIC BACTERIA ISOLATED FROM C  26-  1
PHOTOGRAPHY TO MEASURE THE EFFECT  OF TOXICANTS ON THE FEEDING 3EHAVIOR  36-  2
PHOTOPRODUCTS IN A SIMULATED  MARSH  SYSTEM  /.DYNAMICS OF MIREX AND ITS   18-  2
POLLUTANT GRAOIEMTS BY A3UATIC ORGANISMS /.AUTOMATED DEVICE (AGARS) FO  17-  4
POLLUTANTS ON MICROBIAL ACTIVITIES  IN ESTUARIN5 SURFACE FILMS /.EFFECT   1-  2
    11      /.FATE ANO EFFECTS OF POLLUTANTS:  FATE 0~ ENVIRONMENTAL     30-  5
    H        FATE jp ENVIRONMENTAL  POLLUTANTS /.FATE AND EFFECTS OF     30-  5
    «      m TH£ MARINE t^VTRONMEMT /.INTERDEPENDENT MICROCOSMS FOR T   8-1
    "      IN LOTIC STREAM ECOSYSTEMS /.MICROCOSM SYSTEM TO MODEL THE   32-  1
    11      AND KIC300RSAMI-SMS /.USE  OF  MICROCOSMS FOR EVALUATION OF IN  34-  2
    "      IN; wjA^INE ENVIRONMENTS  /.WORKSHOP:  MICROBIAL DEGRADATION 0  11-  3
POLYCHAETA",  AREHICOLIDAE) /.BcNTHIC BIOASSAY USIN3 TIME-LAPSE PHOTOGR  36-  2
POLYCHLORINATED BIPHENYL FORMULATIONS ON THE GROWTH OF ESTUARINE BACTE   5-  2
       H        9IPHPKYL (PCS) WITH  ESTUARINE MICROORGANISMS ANO SHELL  14-  2
       n  -•     8IPHSNYLS /.INHIBITION  OF  ESTUARINE MICROORGANISMS  BY    7-  3
                                    PAGE  57

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                            KEYWORD  TITLE  INDEX                          P   I
                                                                         A   T
                                                                         G   £
                                                                         E   M
                                      P
POLYCHLORINATED SI^HENYLS CPCBS)  IN  HUOSON RIVER  STRIPED BASS,  MORONE   30- 1
       "         SIPHENYL TRAMS?ORT IN  COASTAL  MARINE  FOOOWPBS           29- 1
POPULATIONS IN COASTAL SURFACE SLICKS  /.MICRQBIAL                       19- 1
PREDICTIONS:  STUDIES WITH KEPONE  AND  METHYL PARATHION /,VALIDITY OF PA  16- i
PRINCIPAL ?H3TOP-^OOUCTS IN A SIMULATED  MARSH SYSTEM  /,DYNAMICS  OF MIRE  18- 2
PROBABLE-NUMBER METHOD FOR USE WITH  .\JONPQLAR AMD  VOLATILE  SUBSTRATES /  41- 2
PROBES  DtV:-LOFSD TO DETECT BIOLOGICAL  CONTROL  AGENTS  IN NON-TARGET HOS  45- 1
PROCEDURE /.DENSITIES IF BACTERIA  AND  FUNGI IN COASTAL  SURFACE  FILMS A  18- 3
PROCEEDINGS OF THE WORKSHOP  81'JDeGRADATIQN KINETICS NAVARRE 3EACH, F  11- 1
PROPACHLOR, ALACHL3R, AND CYCLOATE I \i  SEWAGE AND  LAKE WATER /.COMETABQ  28- 1
PROTEASE  FROM SACCHARO'-IYCQPSIS LIPQLYTICA  /.PURIFICATION AND CHARACTER   1- 1
PSEUDOMONAS SPECIES /,METABOLISM  OF  OI3ENZO C1.43DIOXAN 3Y  A            22- 2
PUGIO FROM CONTAMINATED HARBOR SEDIMENTS /.ACCUMULATION OF  PCB,  MERCUR  36- 1
PULP MILL EFFLUENTS /.AVOIDANCE RESPONSES  OF ESTUARINE  ORGANISMS TO ST  24- 1
PURIFICATION  AND CHARACTERIZATION  OF  A  NEUTRAL PROTEASE FROM SACCHARQM   1- 1
                                      R
REDUCING  BACTERIA AND SEDIMENTARY  COMMUNITIES. PH.D. DISSERTATION. /,  20- 1
REGULATORY RESPONSIBILITY                                                11- 2
REPRESENTATIVE ESTJARINE SPECIES  AND  DEVELOPING BENTMIC COMMUNITIES /,  38- 1
RESPIRATION OF SEVERAL ESTUARINE  BACTERIA  /.EFFECTS  OF  KEPONE ON GROWT  25- 2
RESPONSES OF  ESTUARINE ORGANISMS  TO  STORM  WATER RUNOFF  AND  PULP  MILL E  24- 1
RESPONSIBILITY /.REGULATORY                                              11- 2
RIVER STRIPED BASS. II. ACCUMULATION  FROM  DIETARY SOURCES  /.PCB  DYNAMI  29- 3
  "   STRI^EO BASS, MORONE SAXATILIS.   PH.D. DISSERTATION  /.PHARMACOKI  30- 1
RJ-5 AND  JP-9 IN AQUATIC TEST SYSTEMS  /»FATE AND  TQXICITY  OF HIGH DENS  44- 2
RUNOFF AND PUL3 MILL EFFLUENTS /.AVOIDANCE RESPONSES  OF ESTUARINE DRGA  24- 1
  11    /.FIELD AND LABORATORY AVOIDANCE REACTIONS BY  BLUE  CRABS  CCALLI  23- 2
                                      s
S. THESIS /.3IOTIC AMD ABI3TIC FACTORS  AFFECTING  SORPTION  OF TOXIC COM  14- 1
  GUIDE =C8 WASTuX, A FRAMEWORK i=QR  MODELING THE  FATE OF TOXIC  CHEMICA  15- 1
SACCHAROMYCOPSIS LIP3LYTICA /.PURIFICATION AND CHARACTERIZATION  OF A N   1-1
SALINITY, TEMPERATURE, AND STERILITY  /, INSECTICIDE PERSISTENCE  IN MATU  47- 1
SALT MARSH SYSTEM /.APPARATUS TD  PRODUCE TIDAL FLUCTUATIONS IN  A SIMUL  17- 3
 "   MARSH ENVIRONMENT /.ARTIFICIAL  MICRSBIAL  ECOSYSTEM ^OR DETESMININ   3- 4
 11   MARSH MICROORGANISMS /.DEGRADATION OF M.ALATHION  BY                  4- 2
 "   MARSH ENVIRON^FfJT /.EFFECTS  OF  MALATHION  ON  MICROORGANISMS  OF AN    6- 1
 11   MARSH ENVIRONMENTS:  RESULTS  FROM  A FIELD APPLICATION  (ABSTRACT)   27- i
 "   M^RSH ECOSYSTEMS—EFFECT AND  DEGRADATION  /, MICROBIAL-MAL ATHION IN   9- 1
SALTWATER HOLDING TANKS /.DEVICE  TO  DETECT POTENTIALLY  DANGEROUS ELECT  18- 1
SAPIDUS)  TO STOP1 WATER RUNOFF /.FIELD  AND LABORATORY AVOIDANCE  REACTI  23- 2
SAXATILIS.  PH.D. DISSERTATION /.PHARMACOKINETICS AND DISTRIBUTION OF   30- 1
SCREENING TEST /.DEVELOPMENT OF a  FATE/TOXICITY                          46- 1
SEA /.ISOLftTIOiJ OF ATYPICAL CANDIDA  AL'UCANS FROM THE NORTH             18- 4
 "  AND AMOCO CADIZ OIL /,YEASTS  F30M  THE  NORTH                           3- 1
SEAGRASS  Q^J KEPONE 
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                             KEYWORD  TITLE  INOEX                         P    I
                                                                         A    T
                                                                         3    €
                                                                         E    M
                                      S
SEDIMENTS ON REPRESENTATIVE  ESTU^RINS SPECIES ANO DEVELOPING BENTHIC C  38-  1
SEED  CULTURES IN THE AQUATIC  ENVIRONMENT /.IMPACT OF MICR03IAL           7-  1
SEWAGE AND LAKE -MTER / .COME T A30LISM OF LOU CONCENTRATIONS OF PROPACHL  28-  1
SHELLFISH /.EFFECTS AND  INTERACTIONS DF POLYCHLORINATEO 3IPHFNYL (PC3)  14-  2
SIMULATED SALT MARSH SYSTEM  /.APPARATUS TO PRODUCE TIDAL FLUCTUATIONS   17-  3
    "     MARSH SYSTEM  /.DYNAMICS  OF MIREX AND ITS PRINCIPAL PHOTOPROD  18-  2
SLICKS /.MICR03IAL INTERACTIONS  WITH PESTICIDES IN ESTUARINE SURFACE     2-  1
  "    /.MICR03I4L POPULATIONS IN  COASTAL  SURFACE                       19-  1
SODIUM PENTACHLOROPHENATE  ON  THE FEEDING ACTIVITY OF THE LUGWQRM, AREN  37-  2
SORPTION CF TCXIC COMPOUNDS  TO NATURAL  SEDIMENTS,  M.S. THESIS /.BIOTI  14-  1
SOURCE BY A DEMERSAL PISH  (LcIOSTOMUS XANTHURUS) /.DIETARY ACCUMULATIO  37-  1
SOURCES /,PC3 DYNAMICS  I?J  HUDSON RIVER  STRIPED BASS. II. ACCUMULATION   29-  3
SPOIL MATERIAL IM THE 3C?AM  3NO  THE  PCS CONTAMINATION ISSUE CSTATEMENT  28-  3
STERILITY /.INSECTICIDE  PERSISTENCE  IN  NATURAL SEAWATER AS AFFECTED BY  47-  1
STIMPSON /.EFFECT OF S3DIUM  PENTACHLOROPHENATE ON THE FEEDING ACTIVITY  37-  2
STORM WATER RUNC=F AND  PULP  MILL EFFLUENTS /.AVOIDANCE RESPONSES OF ES  24-  1
   "   w'ATER RUNOFF /.FIELD AND LABORATORY AVOIDANCE REACTIONS 8Y BLUE   23-  2
STREAM ECOSYSTEMS /.MICROCOSM SYSTEM TO MODEL THE FATE AND EFFECTS OF   32-  1
STRIPED 3ASS. II. ACCUMULATION FROM  DIETARY SOURCES /,PCS DYNAMICS IN   29-  3
   "    3ASS, M03QME SAXATILIS.  PH.D.  DISSERTATION /,PHARMACQKINETICS  30-  1
STRUCTURE /.ADAPTATION  OF  NATURAL  MICRDBIAL COMMUNITIES TO DEGRADATION  41-  3
SUBSTRATE CONCENTRATION AND  ORGANIC  AND INORGANIC COMPOUNDS ON THE OCC  47-  3
SUBSTRATES  ON THE SIOCcG^AOATION OF  ORGANIC COMPOUNDS AT LOW CONCENTRA  39-  1
     "       ON BIQDEGRADATION Or  MONOSU3STITUTED PHENOLS BY AQUATIC BAC  40-  1
     "       /.MODIFICATION  DF THE 14C MOST-PROBABLE-NUM3ER METHOD FOR U  41-  2
SULFATE-RE2UCING BACTERIA  AND SEDIMENTARY COMMUNITIES.  PH.D. OISSERTA  20-  1
SURFACE FILMS AS DETERMINED  BY  A MEMBRANE-ADSORPTION PROCEDURE /.DENSI  18-  3
   11    FILMS /,SF = ECTS OF POLLUTANTS ON HICR03IAL ACTIVITIES IN ESTUA   1-  2
   "    SLICKS /.MTCRQ^IAL INTERACTIONS WITH PESTICIDES IN ESTUARINE     2-  1
   11    SLICKS /.MICR03IAL POPULATIONS  IN COASTAL                       19-  1
   11    MICROLAY5RS /,MICROBIOLOGY AND  CHEMISTRY OF ESTUARINE           10-  1
SYNOPSIS 0= DISCUSSION  SESSION:  EXTRAPOLATION                          33-  2
                                      T
TANKS /.DEVICE TO DETECT POTENTIALLY DANGEROUS ELECTRICAL CURRENTS IN   18-  1
TARGET HOSTS /, P 2>T HOLOGIC, BIOCHEMICAL  AND GENETIC PROSES DEVELOPED TO  45-  1
TEMPERATURE, AMD STERILITY /.INSECTICIDE PERSISTENCE IN NATURAL SEAWAT  47-  1
TEST  SYSTEMS /.COMPARISON  2F P-NTTROPHFNOL BIOOEGRADATION IN FIELD AND  42-  2
  "    SYSTEMS /.DEGRADATION OF SELECTED  XtNOBIOTIC COMPOUNDS IN THREE T  45-  2
  "    /.DEVELOPMENT OF A FATE/TOXICITY SCREENING                         46-  1
  "    SYSTEMS /.FATE AND TOXICITY OF  HIGH DENSITY MISSILE FUELS RJ-5 AN  44-  2
  "    SYSTEMS FROM FRESHWATER AMD ESTUA3IME SITES /,FAT= OF METHYL PARA  31-  1
TESTING /,5VALUATI3N 0? THREE FISH SPECIES AS 3IOASSAY ORGANISMS FOR D  38-  2
THESIS /.3IQTIC AND ABIOTIC  FACTORS  AFFECTING SORPTION QF TOXIC COMPOU  14-  1
TIDAL FLUCTUATIONS IN A SIMULATED  SALT  MARSH SYSTEM /.APPARATUS TO PRO  17-  3
TIME-LAPSE  PHOTOGRAPHY  TO  MEASURE  THt EFFECT OF TOXICANTS ON THE FEEDI  36-  2
TOXIC COMPOUNDS TO NATURAL SEDIMENTS.  M.S. THESIS /.8IOTIC AND ABIOTI  14-  1
   11   CHEMICALS IN AQUATIC ENVIRONMENTS, PART 1   EXPOSURE CONCENTRATI  15-  1
                                                   FOOD CHAIN CPROJECT   17-  1
                                                   FOOD CHAIN /.WASTOX,  16-  2
  "    CHEMICALS  IN AQUATIC ENVIRONMENTS,  P^RT  2
  "    CHEMICALS  IN AQUATIC ENVIRONMENTS,  PART  2
TOXICANTS  IN  A SALT-MARSH ENVIRONMENT  /,ARTIFIC  AL  MICR03IAL ECOSYSTEM   3- 4
    11      3N  THE FEEDING BEHAVIOR OF LUGWORMS  
-------
                             KEYWORD  TITLE INDEX                          P    I
                                                                          A    T
                                                                          G    E
                                                                          c    M
                                      U
UPTAKE OF AROMATIC AND BRANCHED  CHAIN HYDROCARBONS 3Y YEAST              19-  2
UREA  /.ANTIMICROBIAL ACTIVITIES  OF  N-CHLORAMTNcS AND DIAZOLIDINYL        24-  2
                                      V
VALIDITY Q- PARTITION COEFFICIENT  4S THF ADSORPTION DESCRIPTOR IN £XPO   16-  1
VARIABILITY OF BIOOEGR4DATION  RATES  OF PESTICIDES IN WATER/SEDIMENT SY   35-  1
VERIFY CHEMICAL FATE ASSESSMENTS;  COMPARISONS OF THE FATE OF METHYL PA   30-  3
VIRENS, MERCENARIA MERCEiJARIA  AND  PALAEMONETES PUGIO FROM CONTAMINATED   36-  1
VITRO ESTUARINS AND  SEDIMENT/WATER  SYSTEMS /,BIOLOGICAL AND ABIOTIC DE   45-  3
VOLATILE SUBSTRATES  /, MODIFICATION  Of TH'5 14C MOST-PROBASLc-NUMBER MET   41-  2
                                      W
WASTOXi A FRAMEWORK  F03  MODELING THE FATE OF TCJXIC CHEMICALS IN AQUATI   15-  1
  »     A FRAMEWORK  =OR  MODELING THE FATE OF T1XIC CHEMICALS IN AQUATI   17-  1
  «     A FRAMEWORK  PCR  MODELING THE FATE OF TOXIC CHEMICALS IN AQUATI   16-  2
MATER SYSTEMS /.APPLICATION  OF MICROCOSM STUDIES TO VERIFY CHEMICAL FA   30-  3
  "   RUMC=F AND  PULP MILL  EFFLUENTS /^AVOIDANCE RESPONSES OF ESTUARIN   24-  1
  «   SYSTEMS /,3IOLOGICAL  ANID ABIOTIC DEGRADATION RATES OF XEN03IOTIC   45-  3
  "   /tCOMETABOLISM GF  LOW  CONCENTRATIONS 0= PROPACHLQR, ALACHLOR, AN   28-  1
  »   CORES FROM  ESTUA7INE  AND FRESHWATER ENVIRONMENTS /^EFFECTS OF AD   44-1
  «   LA3CRATO.RY  SYSTEMS  /,EFFECTS  OF LUGWQRMS AND SEA3RASS ON KEPONE    29-  2
  «   AND SEDIMENT TEST  SYSTEM ^ROH FRESHWATER AND ESTUARINE SITES /,   31-  1
  «   RUNOFF /tFIELO AMD  LABORATORY  AVOIDANCE REACTIONS BY BLUE CRABS    23-  2
  "   INTERFACE IN LAEDRATJRY  SYSTEMS /,MOVEMENT OF KEPONE ACROSS AN U   32-  3
  «   SEDIMENT SYSTEMS  (ABSTRACT)  /.VARIABILITY OF 8IOOEGRADATION RATE   35-  1
                                      X
 XANTHURUS) /,DIETARY ACCJMULATION  OF PC6S FROM A CONTAMINATED SEDIMENT   37-  1
 XENQBIQTIC COKPOUNOSJ   EFFECTS 0=  CONCENTRATION, INOCULUM, AND CHEMICA   41-  3
     11      CHEMICALS IM  IN  VITRO ESTUARINE AND SEDIMENT/WATER SYSTEMS    45-  3
     "      COMPGUNHS IN  ^H^EE  TYPES  OF AQUATIC TEST SYSTEMS /,DEGRADAT   45-  2
     «      COMPOUNDS /,MICROBIAL DcGRAOATION 0"                          8-  3
                                      Y
 YEAST /,UPTAKE OF AROMATIC  AND BRANCHED CHAIN HYDROCARBONS SY            19-  2
 YEASTS  F3R P4TH03ENICITY  /.EVALUATION OF INDUSTRIAL                      21-  2
  11     FROM THE MORTH SEA AND  AMJCQ  CADIZ OIL                            3-  1
                                    PAG£   60

-------
AUTHOR INDEX
   PAGE  61

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                                AUTHOR INDEX
                                      A
ABOELAL,  AHMED T.H.
  PURIFICATION AND CHARACTERIZATION Or A NEUTRAL P-->OTEAS= PROM
  SACCHAROMYCOPSIS LIPilLYT ICA/, 1-1

4HEARN,  DONALD G.
  EFFECTS OF POLLUTANTS  ON  MICRD3IAL ACTIVITIES IN ESTUARINE  SURFACE
  FILMS/t1 ~ 2


  MICROBIAL INTERACTIONS WITH PESTICIDES IN ESTUARINE SURFACE SLICKS/.2-1

  MICROBIOLOGICAL  CYCLING OF  DIL IN ESTUARINE MARSHLANDS/,2-2

  YEASTS FROM THE  MORTH  SEA ANO AMOCO CADIZ OIL/,3-1

ftHEARNt  DONALD G., JOINT AUTHOR.
  ANTIMICROBIAL  ACTIVITIES  OF N-CHLQRAMINES AND OIAZOLIDINYL  UREA/,24-2

  DENSITIES OF BACTERIA  AND FUNGI IN COASTAL SURFACE FILMS  AS DETERMINED  BY  A
  MEMBRANE-ADSORPTION  PROCEDURE/,18-3

  EFFECT OF HEPTACHLQR ON HEXADECANE UTILIZATION BY SELECTED  FUNGI/,41-1

  EFFECTS OF LUGWORMS  4ND SrAGRASS ON KEPONE CCHLORDECON5)  DISTRIBUTION IN
  SEDIMENT/WATER  LABORATORY SYSTEMS/,29-2

  EVALUATION C~  INDUSTRIAL  YEASTS FC3 PATHOGcNlCITY/,21-2

  IMPACT 0<= THE  USE  OF MICROORGANISMS ON THE A3UATIC ENVIRONMENT/,7-2

  INHIBITION GF  rSTUARINE MICROORGANISMS BY POLYCHLO>?INftTED BIPHENYLS/, 7-3

  ISOLATION OF ATYPICAL  CANDIDA AL8ICAfJS FROM THE NORTH SEA/,13-4

  MICROBIAL POPULATIONS  IN  COASTAL SURFACE SLICKS/,19-1

  MICROBICLCGY A'10 CHEMISTRY  OF ESTUARINS SURFACE MICROLAYER S/, 10-1

  MOVEMENT Q? KEPO^E  ACROSS AN UNDISTURBED SEDIMzNT-WATER INTERFACE IN
  LABORATORY SYSTE'IS/, 32-3

  PURIFICATION AND CHARACTSRIZATIQ'-J OF A NEUTRAL PROTEASE FROM
  SACCSAROMYCOPSIS LIPOLYTICA/,1-1

  UPTAKE OF AROMATIC  AND BRANCHED CHAIN HYDROCARBONS B 
-------
                                AUTHCt? INDEX
                                      A
ALEXANDER,  MARTIN, JOINT AUTHOR.
  COMETA30LISM Or LOW CONCENTRATIONS CF PROPACHLDR, ALACHLOR,  AND  CYCLOATE IN
  SEWAGE  AND LAKE UATER/,28-1

  EFFECT  OF SUBSTRATE CTNC 5NTRATION AND ORGANIC AND INORGANIC  COMPOUNDS  ON THE
  OCCURRENCE AMD RATE OF MI N i R AL II iTION AND COMETASQLISM/, 47-3

  EFFECTS OF DISSOLVED  ORGANIC  CARBON AN3 SECOND SUBSTRATES ON  THE
  3IODEGSAQATI IN 0-= ORGANIC  COMPOUNDS AT LOW CONCENTRATIONS/ , 39-1

                                      B
8ARTHA,  R., JOINT AUTHOR.
  DISCUSSI3N:  CONCf°T3 AMD  TR«=NOS  C AQUATIC MICR08IAL ECOLOGY )/,30-2

BELL,  S.L., JOINT AUTHOR.
  UPTAKE  0= AROMATIC  AND BRANCHED CHAIN HYDROCARBONS BY YEAST/,19-2

BERNER,  N.H., JOINT AUTHOR.
  INHIBITION 0=  =STU2RIN£  MICROORGANISMS BY POLYCHLORINATEO 3IPHENYL S/, 7-3

  MICROBIOLOGICAL CYCLING  OF OIL  IN ESTUARINE MARSHLANDS/, 2-2

BOURQUIN, AL W.
  ARTIFICIAL MICR03IAL  ECOSYSTEM  F?DR DETERMINING EFFECTS AMD FATE  OF  TOXICANTS
  IN A SALT-MARSH ENVIRONMENT/, 3-4

  8IODEGRADATION  IM THE ESTU ARINS-MARINE ENVIRONMENTS ANO THE  GENETICALLY
  ALTERED MICROBE/ , 4-1

  DEGRADATION .IF  MALATHION BY SALT-MARSH MICROORGANISMS/,4-2

  DISCUSSION - AQUATIC  MICROBIAL  ECOLOGY/, 4-3

  DISTRIBUTION 0= 3ACT5RIA V;!Tn iNITRILOTRI AC€T AT r-DEGR * DING POTENTIAL IN AN
  ESTUARINE ENVIRONMENT/, 5-1

  EFFECT OF PQLYCHLORI MATED ;.I?HENYL FORMULATIONS QN THE GROWTH OF  ESTUARINE
  BACTERIA/, 5-2

  EFFECTS QF KEPONE ON  ESTUARINE  MICROORGANISMS/, 5-3

  EFFECTS 3F MALATHION  ON  ,-IICRDQRG AN ISMS OF a,N ARTIFICIAL SALT-MARSH
         NE MICROBES  AND O.^GANOCHLORIN= PESTICIDES  CA  BRIEF  REVIEW)/, 6-2

  IMPACT Or MICR08IAL SEED CULTURES IN THE AQUATIC  ENVIRONMENT/, 7-1

  IMPACT OF THE  USE  OF MICROORGANISMS ON THE AQUATIC ENVIRONMENT/,7-2

  INHIBITION  OF  6STUARINE MICROORGANISMS BY POLYCHLORINATED  3IPHENYLS/, 7-3

  INTERDEPENDENT  MICROCOSMS FOR THE ASSESSMENT  OF POLLUTANTS IN  THE  MARINE
  ENVIRONMENT/,8-1

  MICRQ8IAL DEGRADATION OF HALOGENATEO HYDROCARBONS/,8-2
                                    PAGE  63

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                                AUTHOS  INDEX

BOURQUIN,  AL  W.                       B
  MICROBIAL  'DEGRADATION OF XcNOBlOTIC  COMPOUNDS/,8-3

  MICROBIAL-MALATHION INTERACTION  IN  ARTIFICIAL SALT-MARSH ECOSYST^MS—EFFECT
  AND  DEGRADATION/,9-1

  MICROBIOLOGY AND CHEMISTRY  0*  ESTUARINE  -SURFACE  MICROLAYERS/,10-1

  PROCEEDIMGS 3F THE WORKSHRP:   3ID05GRADATION KINETICS NAVARRE 3EACH, FLORIDA
  18-20  OCTOBER 19d3/,ll-I

  REGULATORY  R£SPOMSIBILITY/,11-2

  WORKSHOP:   MICROBIAL  DEGRADATION o-=  POLLUTANTS IN MARINE ENVIRONMENTS/,n-3

BOURQUIN,  AL  W., JOINT  AUTHOR.
  APPLICATION OF MICROCOSM STUDIES TO  VERIFY CHEMICAL FATE ASSESSMENTS;
  COMPARISONS OF THE FATE OF  METHYL PARATHION IN SEDIMENT-WATER SYSTEMS/,30-3

  BIOLOGICAL  AND A3IQTIC  DEGRADATION  RATES 0= XEM03IOTIC CHEMICALS IN IN  VITRO
  ESTUARINE AND SEDIMENT/WATER  SYSTEMS/,45-3

  DEGRADATION OF JET FUEL HYOROCAR30NS BY  AQUATIC MICROBIAL COMMUNITIES:   AN
  INTERIM REPORT 23 OCT03ER  1931 TO 30 SEPTEMBER 1982/,43-l

  DENSITIES OF BACTERIA AND  FUNGI  IN  COASTAL SURFACE FILMS AS DETERMINED  BY A
  MEMBRANE-ADSORPTION! PR DC?CURE/, 18-3

  DEVELOPMENTS IN  INDUSTRIAL  MICROBIOLOGY, VOL. 15/.27-2

  DIBUTYLPHTHALATE DEGRADATION  IN  ESTUARINt ANO FRESHWATER SITES/,46-2

  DISCUSSION:  CONCEPTS AND  TRENDS (AQUATIC MICR08IAL ECOLOGY)/,30-2

  EFFECT CF HEPTACHLOR  ON HEXADECANE  UTILIZATION BY SELECTED FUNGI/,41-1

  EFFECTS JF ADAPTATION ON BIODEGRADATION  RATES IN SEDIMENT/WATER CORES FROM
  ESTUARINE AND FRESHWATER ENVIRONMENTS/,44-1

  EFFECTS OF KEPONE ON  GROWTH AND  RESPIRATION OF SEVERAL ESTUARINE
  BACTERIA/,25-2

  EFFECTS IF LUGWORMS ANO SEAGRASS OM KEPONE (CHLCRDECONE) DISTRIBUTION IN
  SEDIMENT/WATER LABORATORY  SYSTEMS/,23-2

  FATE AND DEGRADATION  Or 14C-KEPONE  IN ESTUARINE MICROCOSMS/,21-1

  FATE OF FENTHIQN 14 SALT MARSH ENVIRONMENTS:  RESULTS FROM A FIELD
  APPLICATION (ABSTRACT)/,27-1

  FATE OF METHYL PARATHION IN WATER AND SEDIMENT TEST SYSTEMS FROM FRESHWATER
  ANO fSTUARINc SITES/,31-1

  MICROBIAL POPULATIONS IN COASTAL SURFACE SLICKS/,19-1

  MICROBIAL TOXICITY STUDIES/,31-2
                                    PAGE  64

-------
                                AUTHOR INDEX
                                      B
BOURQUIN,  AL U., JOINT AUTHOR.
  PERSPECTIVE ON THE RJLc  3F  MICROCOSMS IN ENVIRONMENTAL FATE  AND  EFFECTS
  ASSESSMENTS/,33-1


  PHEN1TLACETIC ACID METABOLISM  BY THREE AQ'JATIC BACTERIA ISOLATED  FROM
  CONTINUOUS CULTURE EMRICHMcNTS/,26-1

  SUCCESSION OF MICROFUNGI  IN ESTUARINt MICROCOSMS PERTURBCD BY CARBARYLt
  METHYL PARATHIQN AND PENTACHLOROPHENOL/,17-2

  SYSTEM DESIGN ^ACTORS AFFECTINS ENVIRONMENTAL PAT£ STUDIES IN
  MICROCOSMS/,34-1

  USE OF MICROCOSMS ^0* EVALUATION OF INTERACTIONS BETWEEN POLLUTANTS AND
  MICROORGANISMS/,34-2

  VARIABILITY OF BIOOE3RADATION RATES OF PESTICIDES IN WATER/SEDIMENT SYSTEMS
  (ABSTRACT)/,35-1

 BOWMAN, P.I., JOINT AUTHOR.
  ISOLATION  OF  ATYPICAL CANDIDA ALBICAMS FROM THE NORTH SEA/,18-4

 BUTLER, L.C., JOINT AUTHOR.
  DEGRADATION 3F JET  FUEL  HYDRJCAR30NS BY AQ'JATIC HICROBIAL COMMUNITIES:   AN
  INTERIM REPORT 23 OCT03E3 1931 TO 30 SEPTEMBER 1982/,43-l

                                      C
 CABELLI, VICTOR J.
  MICROORGANISMS/,12-1

 CARLUCCI, ANGELO F.,  JOINT AUTHOR.
  MICROORGAMISMS/,12-1

 CASSIDY, S., JOINT AUTHOR.
  EFFECT 0-  3CLYCHLORINATEO BIPHENYL FORMULATIONS ON THE GROWTH OF ESTUARINE
  BACTERIA/,5-2

 CERNIGLIA, CARL E.
  3ACTERIAL  AN3 FUNGAL OXIDATION OF OIdEMZOFURAN/,13-1

  SOME APPROACHES  TO  STUDIES ON THE DEGRADATION OF AROMATIC HYDROCARBONS BY
  FUNGI/,13-2

 CHANDLERi F.W., JOINT AUTHOR.
  EVALUATION 0- INDUSTRIAL YSASTS FOS ?ATHOGENICITY/,21-2


 CLESCERI, L.S., JOINT AUTHOR.
  SYNOPSIS OF DISCUS SIGN  SESSION:  EXTRAPOLATION/,33-2

 CLEVELAND, E.,  JOINT  AUTHOR.
  APPLICATION OF MICROCOSM STUDIES TO VERIFY CHEMICAL FATE ASSESSMENTS?
  COMPARISONS OF TIE  FATE  OF METHYL PARATHION IN SEDIMENT-WATER  SYSTEMS/,30-3


 CLEVELAND, MARY E., JOINT  AUTHOR.                           n^^   ,„„„,.
  VALIDITY OF PARTITION COEFFICIENT AS THE ADSORPTION DESCRIPTOR  IN EXPOSURE
  CONCENTRATIONS PREDICTIONS: STUDIES WITH KEPONE ANO METHYL  PARATHION/,16-1
                                    PAGE  65

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                                AUTHOR INDEX
                                      C
CLEVELAND,  MARY ELIZABETH
  BIQTIC AMD ASIATIC FACTORS  AFFECTING SORPTIOM OF TOXIC COMPOUNDS TO  NATURAL
  SEDIMENTS.  M.S. THESIS/,14-1

COLWELL, RITA R.
  EFFECTS AND INTERACTIONS  OF POLYiHLOSINATED 8I°HENYL (PCS) WITH ^STUARINE
  MICROORGANISMS AND SHELLFISH/,14-2

CONNOLLY, J., JOINT AUTHOR.
  APPLICATION OF MICROCOSM  STUDIES  TO VERIFY CHEMICAL FATE ASSESSMENTS!
  COMPARISONS OF TriE FATE  3F  METHYL PARATHION IN SEDIMENT-WATER SYSTEMS/,30-3

CONNOLLY, JOHN P.
  USER'S GUIDE FOR WASTOX,  A  FRAMEWORK FOR MODELING THE FATE Of TOXIC
  CHEMICALS IN A-3UATIC  ENVIRONMENTS, PART 1:  EXPOSURE CONCENTRATION/,15-1

  VALIDITY OF »ARTITIOM  COEFFICIENT AS THE ADS3RPTION DESCRIPTOR IN EXPOSURE
  CONCENTRATIONS PREDICTIONS: STUDIES AIJH KEPONt AND METHYL PARATHION/,16-1

  WASTQX, A FRAMEWORK FOR  MODELING  THE FATE OF TOXIC CHEMICALS IN AQUATIC
  ENVIRONMENTS, ^ART 2:   FOOD CHAIN/,16-2

  WASTOX, A FRAMEWORK CCR  MODELING  THE FATE OF TOXIC CHEMICALS IN AQUATIC
  ENVIRONMENTS, PAST 2'.   FOOD CHAIN (PROJECT SUMMARY)/, 17-1

CONNOLLY, JOHN P., JOINT AUTHOR.
  EFFECT CF CONCENTRATION  OF  ADSQR3ING SOLIDS ON THE PARTITION
  COEFFICIENT/,23-2

  rtOVEMEMT OF KEPONE ACROSS AN UNDISTURBED SSDIMENT-WATER INTERFACE IN
  LABORATORY SYSTEMS/,32-3

COOK, U.L.
  SUCCESSION OF MICROF'JNQI  IN ESTUARINc MICROCOSMS PERTURBED BY CARBARYL,
  METHfL PARAT'-iION AMD  PENTACHLOROPHENQL/,17-2

COOK, W.L., JOINT AUTHOR.
  DENSITIES OF BACTERIA  AND FUNGI IN COASTAL SURFACE FILMS AS DETERMINED BY  A
  MEMBRANE-ADSORPTION PROC£DURc/,13-3

  EFFECTS 3F POLLUTANTS  ON  MICR03IAL ACTIVITIES IN ESTUARINE SURFACE
  FILMS/,1-2

  MICROBIAL INTERACTIONS WITH PESTICIDES IN ESTUARINE SURFACE SLICKS/,2-1

  HICR3BIAL POPULATIONS  IN  COASTAL SURFACE SLICKS/,19-1

CRIPE,  CLAUDE R.
  APPARATUS TO PRODUCE  TIDAL  FLUCTUATIONS IN A SIMULATED SALT MARSH
  SYSTEM/,17-3

  AUTOMATED DEVICE (AGARS)  FOR STUDYING AVOIDANCE OF POLLUTANT GRADIENTS  BY
  AQUATIC ORGANISMS/,17-4

  DEVICE TJ DETECT POTENTIALLY DANGEROUS ELECTRICAL CURRENTS IN  SALTWATER
  HOLDING TANKS/,13-1
                                    PAGE  66

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                                AUTHOR INDEX
                                      C
CRlPEt  CLAUDE R.
  DYNAMICS OF HIRcX AND  ITS  PRINCIPAL PHQTQPROOUCTS IN A SIMULATED  MARSH
  SYSTEM/,18-2

CRIPEf  CLAUDE R., JOINT  AUTHOR.
  AVOIJAIMCE RESPONSES  IF ESTUARINE ORGANISMS TO STORM WATER  RUNOFF  AND  PULP
  MILL  EFFLUENTS/,24-1

  BIOLOGICAL AND ABIOTIC DEGRADATION RAT?S OF XEN03IQTIC CHEMICALS  IN IN  VITRO
  ESTUARIN; AND SCOIV.E^T/WATSR SYSTEMS/,45-3

  COMPARISON OF P-MITROPHENOL 3IODEGRADSTION IN FIELD AND LABORATORY TEST
  SYSTEMS/,42-2

  DIBUTYLPriTHALATE  DEGRADATION IN ESTUARINE AND FRESHWATER SITES/,46-2

  FATE OF METHYL PARATHIQN IH WATER AND SEDIMENT TEST SYSTEMS  FROM  FRESHWATER
  AND ESTUARINE SITES/,31-1

  FIELD .AND LABORATORY AVOIDANCE REACTIONS BY 3LUE CRABS < C ALLINECTES SAPIDUS)
  TO STORM WUER R'JNOFc/,23-2

  INTERDEPENDENT MICROCOSMS  FCR THE ASSESSMENT OF POLLUTANTS IN  THE MARINE
  ENVIRONMENT/,8-1

  MICROCOSM  SYSTEM  TO MODEL  TH= FATE AND EFFECTS OF P-CRESOL AMD OTHER
  POLLUTANTS  IN LOTIC STREAM ECOSYSTEMS/,32-1

  REACTIONS  OF  BLUE CPUBS TO LOW PH.  COMMENTS./»23-3

  VARIABILITY  OF BIOOEGP AOC.T ION RATES OF PESTICIDES IN WATER/SEDIMENT SYSTEMS
  (ABSTRACT)/,35-1

 CRIPE, R., JOINT AUTHOR.
  APPLICATION  DF MICROCOSM STUDIES TO VERIFY CHEMICAL ?=ATE ASSESSMENTS?
  COMPARISONS  DF THE  F:\TE OF METHYL PA-7ATHION IN SEDIMENT-WATER  SYSTEMS/, 30-3

 CROW, S.A.
  DENSITIES  OF  BACTERIA AND  FUNGI IN COASTAL SURFACE FILMS AS  DETERMINED  BY A
  MEMBRANE-ADSORPTION PR3CEDURE/,18-3

  ISOLATION  OF  ATYPICAL CANDIDA AL3ICANS FROM THE NORTH SEA/,18-4

  MICRGBIAL  PCDULATI3NS IN COASTAL SURFACE SLICKS/,19-1

  UPTAKE  Or  AROMATIC  AMD BRANCHED CHAIN HYDRDC1R80NS BY YEAST/,19-2

 CROW, S.A.,  JOINT AUTHOR.
  EFFECT  OF  HE^TaCHLQR ON HEXADECAN? UTILIZATION BY SELECTED FUNGI/,41-1

  EFFECTS DF  POLLUTANTS ON MICR03IAL ACTIVITIES IN ESTUARINE SURFACE
  FILMS/,1-2

  INHI3ITION  CP ESTUARINE MICROORGANISMS BY PCLYCHLORINATED  3IPHENYLS/,7-3

  MICROBIAL  INTERACTIONS WITH PESTICIDES IN ESTUARINE SURFACE  SLICKS/,2-1
                                    PAGE  67

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                                AUTHOR INDEX
                                      C
CROW*  S.A., JOINT AUTHOR.
  MICROBIOLOGICAL CYCLING  OF  OIL IN tSTUARlNc MARSHLANDS/,2-2

  YEASTS FW-1 THE MORTH  SE^  AND AMOCT CADIZ OIL/,3-1

                                      0
D'ASARO, CHARLES N.f  JOINT AUTHOR.
  EFFECTS DF CONTAMINATED  SEDIMENTS UN REPRESENTATIVE -STUARIN^ SP-CIES  AND
  DEVELOPING 8ENTHIC  C3MHUNITI6S/,38-1

DODGE, ROBERT H., JOINT  AUTHOR.
  SOME APPROACHES TO  STUOI5S  CM THE DEGRADATION OF AROMATIC HYDROCARBONS  BY
  FUNGI/il3-2

                                      F
FIEDLER, DENISE, JOINT AUTHOR.
  SUCCESSION 0^  -1ICR JF'JNGI IN SSTUARINE MICROCOSMS PERTURBED BY CARBARYL,
  METHYL PARATHION  AND P£NTAChLQ30PH£NOL/»17-2

FREDRICKSON, HERBERT  L.,  JOINT  AUTHOR.
  SYSTEM DESIGN  FACTORS  AFFECTING ENVIRONMENTAL "ATE STUDIES IN
  MICROCOSMS/,34-1

FREDRICKSON, HERBERT  LOWRY
  FATTY ACID CHARACT£RIZATIONS  0- SELECTED SUL^ATE-PEDUCING BACTERIA AND
  SEDIMENTARY COMMUNITIES.  PH.D. DISSERTATION,/,20-1

                                      G
GARNAS, RICHARD  L.
  FATE AND DEGRADATION OF  14C-KEPONE IN ?STUARIN
-------
                                AUTHOR INDEX
                                      G
GlLLIAMt  W.T., JOINT  AUTHOR.
  EVALUATION OP THxEE  = ISH  SPECIES AS 3IOASSAY ORGANISMS  FOR  DREDGED MATERIAL
  TESTING/,38-2


  FATE OF FENTHION IM  SALT  MARSH ENVIRONMENTS:  RESULTS "ROM  A  FIELD
  APPLICATION (ABSTRACT)/,27-1

GREGORY,  N.R., JOINT  AUTHOR.
  ACCUMULATION OF PCS,  MERCURY AMD CADMIUM 8Y NEREIS  VIRENS,  MERCENA3IA
  MERCENARIA AND PAL.AE'-IONETES PUGIO FROM CONTAMINATED  HARBOR  SEDIMENTS/, 36-1

  DIETARY ACCUMULATION  OF  PC3S FROM A CONTAMINATED  SEDIM-NT SOURCE  BY A
  DEMERSAL FISH (LtlOSTOMUS XANTHU3US)/,37-1

  EVALUATION OF THREE  FISH  SPECIES AS 8IOASSAY ORGANISMS  FOR  DREDGED MATERIAL
  TESTING/,33-2

                                      H
HEBERT, RICHARD L.,  JOINT  AUTHOR.
  SOME APPROACHES TO  STUDIES  O'-l THE DEGRADATION OF  AROMATIC HYDROCARBONS BY
  rUNGI/,13-2

HOLZSCHU, D.L.
  EVALUATION 0= IN-OUST3I AL  YEASTS FOR PATHQGtNICITY/f21-2

HOOD, MARY A., JOINT.AUTHOR.
  ARTIFICIAL MICRC3TAL ECOSYSTEM FOR DETERMINING  EFFECTS  AMD  FATE  OF TOXICANTS
  IN  A SALT-MARSH ENVI-1QMMFNT/,3-4

                                      K
KENNEDY, EMILY H.,  JOINT AUTHOR.
  PURIFICATION A'JC  CHARACTERIZATION OF A NEUTRAL  PROTEASE  FROM
  SACCHAROMYCOPSIS  LI POLYT1C A/,1-1

KIEFER, L.A., JOINT  AUTHOR.
  INHIBITION  C? ESTUA
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                                AUTHOR INDEX
                                      L
LAUGHLIN,  ROGER A.
  FIELD  AND LA-iORATORY  AVOIDANCE  REACTIONS BY SL'JE CRASS (CALLINECTES  SA?IDUS)
  TO  STORM WATER RJNQFF/,23-2


  REACTIONS OF BLUE CRABS  TO LOW  PH.   COMMENTS./,23-3

LAUGHLIN,  ROGER A., JOINT  AUTHOR.
  AVOIDANCE RESPONSES  OF  ESTUARIdE ORGANISMS TO STORM WATER RUNOFF AND  PULP
  MILL EFFLUENTS/,24-1

LEE,  T.J., JOINT AUTHOR.
  DEGRADATION OF JET  FUEL  HYDROCARBONS 6Y AQUATIC MICROBIAL COMMUNITIES:   AN
  INTERIM REPORT 23 OCTOBER  1981  TO 30 SEPTEMBER 1982/.43-1

LEWIS, FRANK G., III,  JOINT  AUTHOR.
  AVOIDANCE RESPONSES  OF  ESTUARINE ORGANISMS TO STORM WATER RUNOFF AND  PULP
  MILL EFFLUENTS/,24-1

LITCHFIELD, CAROL D.,  JOINT  AUTHOR.
  MICRQORGAN IS IS/,12-1

LIVINGSTON, ROBERT  J.
  AVOIDANCE RESPONSES  3F  ESTUARINE ORGANISMS TO STORM WATER RUNOFF AND  PULP
  MILL E-FLUENTS/,24-1

LIVINGSTON, ROBERT  J.,  JOINT AUTHOR.
  DYNAMICS OF MISEX AND ITS  PRINCIPAL PHOTQPROOUCTS IN A SIMULATED MARSH
  SYSTEM/,13-2

  FIELD AND LABORATORY AVOIDANCE  REACTIONS BY 3L'JE CRABS (CALLINECTES  SAPIOUS)
  TO  STORM WATER RUNOFF/,23-2

  REACTIONS OF  BLUE CR1DS TO LOW  PH.   COMMENTS./,23-3


LLABRES, CARLOS M.
  ANTIMICROBIAL ACTIVITIES OF  N-CHLQRA?4INES AND DIAZDLIDINYL UREA/,24-2


LORES, EMILE M., JOINT AUTHOR.
  ACCUMULATION  Or  PC3,  MERCURY AND CADMIUM 3Y MEREIS VIRENS, MERCENARIA
  MERCENARIA AND PftLAEMCNETES  PUGIQ CROM CONTAMINATED HARBOR SEDIMENTS/,36-1


LUCYSZYN, E.
  CHARACTERISTICS OF  BACTERIA  4DAPTEO TO LOW NUTRIENT CONDITIONS IN LAKE
  ONTARIO/,25-1

                                      M
MADSEN, EUGENE  L.,  JOINT  AUTHOR.
  SIODEGRADATION BY MINERALIZATION OR COMETA80LISM DETERMINED 3Y CHEMICAL
  CONCENTRATION AND ENVISONMf:NT/,47-2


MAHAFFEY, M.R.
  EFFECTS DF KcPONE ON GROWTH  AND RESPIRATION OF SEVERAL ESTUARINE

  BACTERIA/,25-2

  PHENYLACETIC  ACID METABOLISM 8Y THREE AQUATIC BACTERIA ISOLATED FROM
  CONTINUOUS CULTURE  ENRICHMENTS/,26-1
                                    PAGc  70

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                                AUTHOR INDEX
                                      M
MAHAFFEY,  W.R., JOINT AUTHOR.
  EFFECTS  OF K£PONE ON  CSTUARINE  MICROORGANISMS/,5-3

HAZIARZ,  T., JOINT AUTHOR.
              ^c *ICROCQSK  STUDIES TO VERIFY CHEMICAL FATE ASSESSMENTS;
              OF THE FATE  OF  MfTHYL PARATHIQN IN SEDIMENT-WATER SYSTEMS/,30-3

  SYSTEM  DESIGN FACTORS  AFFECTING 5N VIRQNM'NTAL =ATE STUOI = S IM
  MICROCOSMS/,34-1

METCALF,  THEODORE G.t JOINT AUTHOR.
  MICROORGANISMS/,12-1

HEYERSt SAMUEL P., JOINT AUTHOR.
  IMPACT  OF THE US5  IF  MICROORGANISMS QN THE AQUATIC ENVIRONMENT/,7-2

  MICROBIOLOGICAL CYCLING  OF  OIL  IN ESTUARINc MARSHLANDS/,2-2

MONTI, CAROL A., JOINT  AUTHOR.
  COMPARISON OF P-NITROPHENOL 3IOD=G?AOATIQN IN ^ISLO AND LASORATQRY TEST
  SYSTEMS/,42-2

  EFFECTS OF LUGWO-1MS AMD  SEAGRASS ON KEDONE (CHLQROECONE) DISTRIBUTION IN
  SEDIMENT/WATER LABORATORY SYSTEMS/,29-2

  MODIFICATION OF THc 14C  MOST-PROBABLc-NUMBSR METHOD FOR USE WITH NONPOLAR
  AND VOLATILE SUBSTRATES/,41-2

  MOVEMENT OF KEPO^E ACROSS AN  UNDISTU^PED SEDIMENT-WATER INTERFACE IN
  LABORATORY SYSTEMS/,32-3

MORGAN, JOSEPH C., JOINT AUTHOR.
  3ACTERIAL AND FUNGAL  OXIDATION  OF 013ENZ3FJRAN/,13-1

MUELLER,  LEN H.
  FATE OF =ENTHION IN SALT  MARSH  ENVIRONMENTS:  RESULTS FROM A FIELD
  APPLICATION /,2 3-3
                                    PAGE  71

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                                AUTHOR INDEX
                                      0
O'CONNOR,  JOSEPH M.
  POLYCHLCRINATEO 3IPH2NYL  TRANSPORT IN COASTAL MARINE FOQOW53 S/ ,2 9-1

O'CONNOR,  JOSEPH M. , JOINT  AUTHOR.

                * HU°SON  RIVER  STRIP£D EA*S. II. ACCUMULATION  FROM  DIETARY
O'NEIL,  ELLEN J.
  EFFECTS  OF LUGtfOSMS  AND  SEAGRASS ON KEPONE (CHLQSDECON=) DISTRIBUTION  IN
  SEDIMENT/WATER LABORATORY  SYSTEMS/, 2 ?- 2

O'NEILL, ELLEN J,, JOINT AUTHOR.
  MOVEMENT OF itEPDME ACROSS  AN UNDISTURBED SEDIM€NT-WATER INTERFACE  IN
  LABORATORY SYSTEMS/f 32-3

                                      P
PARRISH, PATRICK R.t JOINT AUTHOR.
  PROCEEDINGS OF THE WORKSHOP:  3IOOEGRADATION KINETICS NAVARRE BEACH, FLORIDA
  18-2J OCTOBER 1983/,11-1

PFAENDER, FREDERIC K.,  JOINT AUTHOR.
  INFLUENCE  3F EASILY  DEGRADABLE  NATURALLY OCCURRING CARBON SUBSTRATES ON
  3IODEGSADATION OF  MOMCSU5STITUTEQ PHENOLS BY AQUATIC BACTERIA/, 40-1

  INFLUENCE  OF NATURALLY  OCCURRING HUMIC ACIDS ON BIQDSGRAQATIQN OF
  MONQSU3STITUTED  PHENOLS  BY A3U-UIC BACTERIA/,40-2

PIERCE, ROBERT J., JOINT  AUTHOR.
  EXPLORING  THr VARIOUS 1SPECTS RELATED TO THE DUMPING QF DREDGEO  SPOIL
  MATERIAL  I\< TH:  '?CEA'J 4NO THE ?C3 CONTAMINATION ISSUE (STATEMENT)/, 23-3

PIZZA, JOHN  C.
  ?C3 DYNAMICS IN  HUDSON  RIVER STRIPcD BASS. II. ACCUMULATION  FROM DIETARY
  SOURCES/,29-3

  PHARMACCKINETICS AMD DISTRIBUTION OF DIETARY POLYCHLORIN ATtD BIPHENYLS
  (PCBS) IN  HUDSON RIVER  STRIPED  BASS, MORONS SAXA.TILIS.  PH.D,
  DISSERTATION/, 30-1

PRAMER, D.
  DISCUSSION:  CONCEPTS AMD TRENDS (AQUATIC MICROBIAL ECOLOGY)/, 30-2

PRITCHARD, PARMELY H.
  APPLICATION OF MICROCOSM STUDIES TO VERIFY CHEMICAL FATE ASSESSMENTS?
  COMPARISONS OF THE FSTc  OF METHYL PARATHION IN SEDIMtNT-WATER SYSTEMS/ , 30-3

  ASSESSING  THE 3IODEGSADA TI ON OF SEDIMENT ASSOCIATED CHEMICALS/,30-4

  FATE AND EFFECTS OF  =>OLLUTANTS:  FATE OF ENVIRONMENTAL POLLUTANTS/,30-5

  FATE OF METHYL PARATHI3M IN UATE^ AND SEOIMENT T=ST SYSTEMS  FROM FRESHWATER
  AND ESTUARINE SITES/,31-1

  MICR03IAL  TOXICITY STUDIES/, 31-2

  MICROCOSM  SYSTEM TO  MODEL  THE FATE AND EFFECTS OF P-CRESOL AND OTHER
  POLLUTANTS IN LOTIC  "TOE'M ECOSYSTEMS/,32-1
                                          72

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                                AUTHOR INDEX
                                      P
PRITCHARD,  PARMELY H.
  MODEL  ECOSYSTEMS/, 32-2

  MOVEMENT  OF KEPONE ACROSS  AN  UMCT STUBBED SEDIMENT-WATER INTERFACE  IN
  LABORATORY SYS TEMS/ , 32-3

  PERSPECTIVE OH THE ROLE  OF MICROCOSMS IN ENVIRONMENTAL FflTE AND EFFECTS
  ASSESSMENTS/, 33-1

  SYNUPSIS  OF DISCUSSION  SESSION:   EXTRAPOLATION/, 33-2

  SYSTEM DESIGM FACTORS AFFECTING  ENVIRDNM=NTA<  FATE STUDIES IN
  MICRJCOSMS/,34-1

  USE OF MICROCOSMS FOR EVALUATION QP INTERACTIONS BETWEEN POLLUTANTS AND
  MICRO ORGANISMS/, 34 -2

  VARIABILITY OF 8IODEGR 4DATION RATES OF PESTICIDES IN WATER/SEDIMCNT SYSTEMS
  (ABSTRACT)/, 35-1

 PRITCHARD,  PARMELY  H.,  JOINT AUTHOR.
  BIOLOGICAL AND A3I3TIC  DEGRADATION RATES OF XENGdIOTIC CHEMICALS IN IN VITRO
  ESTUARINE AND SEDI -1EMT/W AT ER  SYSTEMS/,45-3

  CHARACTERISTICS  OF 31CTESIA ADAPTED TO L3W NUTRIENT CONDITIONS IN  LAKE
  ONTARIO/,25-1

  COMPARISON 0= P-.^ITROPHENOL 5IOOEGR AOATION IN FIELD AND LABORATORY TEST
  SYSTEMS/,42-2

  OI8UTYLPHT4ALATE  DEGRADATION  IN  ESTUARIME AMI FRESHWATER SITES/,46-2

  EFFECTS  OF ADAPTATION  IN C IOOEGR ADATION SATES IN SEDIMENT/WATER CORES FROM
  ESTUARINE ANO FRESHWATER ENVIRONMENTS/ , 44-1

  EFFECTS  J3F KEPQNE ON  ESTUARINE MICROORGANISMS/,5-3

  EFFECTS  OF KEPON- ON  GROWTH *ND  RESPIRATION OF SEVERAL ESTUARINE
  BACTERIA/, 25-2

  EFFECTS  3F LUGKORMS  AND SEAGRASS ON KEPONE CCHLORDECONE) DISTRIBUTION IN
  SEDIMENT/WATER LABORATORY  SYSTEMS/, 2 9-2

  FATE AMD DEGRADATION  OF 14C-KEPOME IN ESTUARINE MICROCOSMS/ , 21-1

  FATE OF  =ENTHI3N  IM  SALT MARSH ENVIRONMENTS:  RESULTS FROM A FIELD
  APPLICATION (ABSTRACT)/, 27-1

  INTERDEPENDENT MICROCOSMS  FO? THE ASSESSMENT OF POLLUTANTS IN THE  MARINE
  ENVIRONMENT/, 8-1

  MICRQBIAL OESRaOATIOM  DF XSN3BIOTIC COMPOUNDS/, 8-3
  NICRDORGANISMS/,12-1

  PHENYLACSTIC  ACIO  META30LISM BY THREE  AQUATIC BACTERIA  ISOLATED  FROM
  CONTINUOUS  CULTURE ENRICHMENTS/,26-1
                                    PAGE  73

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                                AUTHOR INDEX
                                      P
PRITCHARO,  PARMELY H., JOINT  AUTHOR.
  PROCEEDINGS OF T :-i£ WORKSHOP:   31ODEG?AOATION KINETICS NAVARRE 3EACH,  FLORIDA
  18-20  OCT03ES 1933/,il-l

  VALIDITY  OF PARTITION! COEFFICIENT AS THE ADSORPTION DESCRIPTOR IN EXPOSURE
  CONCENTRATIONS PREDICTIONS:  STUDIES WITH KcPQNE AND METHYL PARATHION/,16-1

  WORKSHOP:  KICSOSIAL DEGRADATION  OF POLLUTANTS IN MARINE ENVIRONMENTS/,11-3

PRZYBYSZEWSKI, V.A., JOINT  AUTHOR.
  DISTRIBUTION OF BACTERIA  WITH NITRILOTRIACETATE-DEGRADING POTENTIAL IN AN
  ESTUARINE ENVIRONMENT/,5-1

                                      R
RUBINSTEIN, NORMAN I.
  ACCUMULATION OF PC3, MERCURY  AND  CADMIUM BY NEREIS VIRENS, M5RCENARIA
  MERCENARIA AND PALAEMQNETES PUGIO FROM CONTAMINATED HARBOR SEDIMENTS/,36-1

  BENTHIC BIOASSAY USING  TIME-LAPSE PHOTOGRAPHY 19 MEASURE THE EFFECT OF
  TOXICANTS ON THF FtEDING  BEHAVIOR OF LUGWORMS (PQLYCHAETA:
  ARENICOLTDAE)/,3S-2

  DIETARY ACCUMULATION OF PCBS  F30M A CONTAMINATED SEDIMENT SOURCE BY A
  DEMERSAL  FISH (LEIQSTOMUS X.AMTHURUS)/, 37-1

  EFFECT OF 5031'JM PENTACHLORCPH'ENATE ON THE FEEDING ACTIVITY OF THE LUGWORM,
  ARENICOLA CRISTATA STIMPSON/,37-2

  EFFECTS OF CONTA 1INATEO  SEOIMEMTS HN REPRESENTATIVE SSTUARINE SPECIES AND
  DEVELOPING BENTHIC COMMUNITIES/,38-1

  EVALUATION Oc TH'
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                                AUTHOR INDEX
                                      S
SOMERVILLE,  C.C.
  MODIFICATION OP THE 14C  MOST-P308A3LE-NUHBER METHOD FOR USE WITH NONPOLAR
  AND  VOLATILE SUBSTRATE$/,41-2

SOMERVILLE,  C.C.t JOINT AUTHOR,
  BIODEGRA3ATION OF JFT FUEL  6Y AQUATIC MICROBIAL COMMUNITIES/,42-1

  DEGRADATION OF JET FUEL  HYDROCARBONS BY AQUATIC MICRQBIAL COMMUNITIES:  AN
  INTERIM REPORT 23 OCTOBER  1991 TO 30 SEPTEMBER 19827,43-1

  FATE AND TOXICITf OF HIGH  DENSITY MISSILE FUELS RJ-5 AND JP-9 IN AQUATIC
  TEST SYSTEMS/,44-2

SOMMERSt C.A., JOINT AUTHOR.
  EFFECTS 3F CONTAMINATED  SEDIMENTS ON R5P3ESEMTATIV5 ESTUARINE SPECIES AND
  DEVELOPING 6ENTHIC COMMUNITIES/t38-1

SPAIN, JIM C.
  ADAPTATION G~ NATURAL  MICROBIAL COMMUNITIES TO DEGRADATION OF XEN09IOTIC
  COMPOUNDS:  -FPECTS  DF  CONCENTRATION, INOCULUM, AND CHEMICAL STRUCTURE/,41-3

  8IODEGRAQATI3N OF JET  FUtL BY AQUATIC MICROBIAL COMMUNITIES/,42-1

  COMPARISON QP °-">iITROPHENOL 5IODEGRADATION IN FIELD AND LABORATORY TEST
  SYSTEMS/,42-2

  DEGRADATION OF J5T  FUEL  HYDROCARBONS BY AQUATIC MICROBXAL COMMUNITIES:  AN
  INTERIM REPORT 23 OCTOBER 1931 TO 30 SEPTEMBER 1982/,43-l

  EFFECTS JF  ADAPTATION  ON BIODEGRADATION SATES IN SEDIMENT/WATER CORES FROM
  5STUARINE  AND FRESHWATER ENVIRONMENTS/,44-1

  FATE AND TOXICITY 3F  HIGH DENSITY MISSILE FUELS RJ-5 AMD JP-9 IN AQUATIC
  TEST SYSTEMS/,44-2

 SPAIN, JIM C.,  JOINT  AUTHOR,
  DEGRADATION OF SELECTED  XEN08IQTIC COMPOUNDS IN THREE TYPES  OF AQUATIC TEST
  SYSTEMS/,4.5-2

  FATE Oc METHYL PARATHI3N IN WATER AND SEDIMENT TEST SYSTEMS  FROM FRESHWATER
  AND ESTUARINF SITES/,31-1

  MICROBIAL  DEGRADATION  OF XrNOBIOTIC COMPOUNDS/»8-3

  MODIFICATION  OF TH7f  14C  MOST-PROBABLc-NUHB cR METHOD FOR USE  WITH NONPOLAR
  AND VOLATILE  SUBSTRATES/,41-2

 STOKES, B.E., JOINT AUTHOR.
  DEVICE TO  DETECT  POTENTIALLY DANGEROUS ELECTRICAL CURRENTS IN SALTWATER
  HOLDING TANKS/,13-1

 SUBBA-RAO, R.V., JOINT  AUTHOR.
  EFFECT OF  SUBSTRATE  CONCENTRATION AND ORGANIC  AND INORGANIC  COMPOUNDS  ON  THE
  OCCURRENCE AND RATE  3F  MINERALIZATION 4NO COMETABOLISH/,47-?

 SUMMERS, MAX
  PATHOLOGIC, BIOCHEMICAL  AND GENFTIC PROBSS DEVELOPED T3 DETECT  BIOLOGICAL
  CONTROL AGENTS IN NON-TARGET HOSTS/,45-1

                                    PAGE  75

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                                AUTHOR  INDcX

 SZANISZLO,  PAUL J.t JOINT AUTHOR.
  SOME  APPROACHES TO STUDIES DM  THE  DEGRADATION  OF  AROMATIC HYDROCARBONS BY
  FUNGI/,13-2

                                      T
 THOMANN,  ROBERT V.f JOINT AUTHOR.
  MASTOX,  A FRAMEWORK = 0* MODELING THE FATE  OF TOXIC  CHEMICALS IN AQUATIC
  ENVIRONMENTS, PART 2:  FOOD CHAI =-]/, 1 S-2

  UASTOX,  A =RAM€W3RK FOR MODELING THE FATE  OF TOXIC  CHEMICALS IM AQUATIC
  ENVIRONMENTS, PART 2:  FOOD CHAIN  (PROJECT SUMMARY)/,17-1

                                      V
 VAN VELD,  P.A.
  DEGRADATION OF SELECTED XENQBIQTIC COMPOUNDS IN  THREE  TYPES OF AQUATIC TEST
  SYSTEMS/,45-2

 VAN VELD,  P.A., JOINT AUTHOR.
  ADAPTATION OF rtATU^AL  MICRDBIAL  COMMUNITIES TO DEGRADATION OF XEN03IOTIC
  COMPOUNDS:  EFFECTS OF CONCENTRATIJN,  INOCULUM,  AND CHEMICAL STRUCTURE/,41-3

  COMPARISON OF P--JI TR OPHENOL 3IODEGRAOATIOM IN  FIELD AND  LABORATORY TEST
  SYSTEMS/,42-2

                                      W
 WALKER, WILLIAM W.
   BIOLOGICAL AND ABIOTIC DEGRADATION RATES  OF XE-NOBIOTIC CHEMICALS IN IN VITRO
   ESTUARINE AND SEDIMENT/WATER SYSTEMS/,45-3

   DEVELOPMENT OF A FATE/TQXICITY SCREENING  TEST/,46-1

   DI3UTYLPMTHALATE DEGRADATION IN  ESTUARINE  AND  FRESHWATER SITES/,46-2

   INSECTICIDE PERSISTENCE IN NATURAL SEflWATER AS AFFECTED  8Y SALINITY,
   TEMPERATURE, AMD STE3ILITY/,*7-l
i
 WALKER, WILLIAM W., JOINT AUTHOR.
   FATE OF METHYL PARATHIQN  IN WATER  AND  SEDIMENT TEST SYSTEMS FROM FRESHWATER
   AND ESTUARINS SITES/,31-1

   PROCEEDINGS OF HE WORKSHOP:   QI3DEGSAOATIDN KINETICS  NAVARRE BEACH, FLORIDA
   18-20 OCT03ER 1933/tll-l

   VARIABILITY OF BIODEGRADATION  RATES  Or  PESTICIDES IN WATER/SEDIMENT SYSTEMS
   (ABSTRACT)/,35-1

 WANG, YEI-SHUNG
   BIODEGRADATION 3Y LIBERALIZATION  OR  COHETABDLISM DETERMINED 3Y CHEMICAL
   CONCtNTRiTION AND cNVI^OMM'NT/,47-2

   EFFECT OF SUBSTRATE CONCENTRATION  AND ORGANIC  AND INORGANIC COMPOUNDS  ON THE
   OCCURRENCE AND RATE OF MINERALIZATION AND COMSTABOLI5M/,47-3

 WATSON, STANLEY W., JOINT AUTHOR.
  MICROORGANISMS/,12-1

 HILKES, FRANK G.,  JOINT  AUTHOR.
  EFFECTS 3F CONTAMINATED SEDIMENTS  ON RcPRE5=NTATIV£ ESTUARINE  SPECIES  AND
  DEVELOPING BENTHIC COMMUNITIES/,38-1

                                     PAGE  76

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                               AUTHOR INDEX
                                     W
HlLKESt  FRANK G.,  JOINT AUTHOR.
  EXPLORING THE VARIOUS ASPECTS RELATED TO THE DUMPING OF DREDGED  SPOIL
  MATERIAL IN THE OCEAN AND THE PC3 CONTAMINATION ISSUE (STATEMENT)/,28-3

  INTERDEPENDENT MICROCOSMS FOR THH ASSESSMENT OF POLLUTANTS  IN THE  MARINE
  ENVIRONMENT/,8-1

WINFIELD, RICHARD P.t JOINT AUTHOR.
  USER'S GUIDE FOR WASTOX, A  FRAMEWORK  FOR MODELING THE FATE  OF TOXIC
  CHEMICALS IN ADUATTC  ENVIRONMENTSf  PART  i:   EXPOSURE CONCENTRATION/,15-1
                                           77

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