TITLE: Biotechnology: Bioremediation
PUBLICATION DATE: August, 1994
ENTRY DATE: September, 1994
EXPIRATION DATE: None
UPDATE: As needed
CONTACT: Biotechnology Information Center(biotech@nalusda.gov)
National Agricultural Library
DOCUMENT TYPE: Text
DOCUMENT SIZE: 197k, approx. 110 pp.

United States Department of Agriculture National Agricultural Library
10301 Baltimore Blvd.
Beltsville, Maryland 20705-2351
Quick bibliography series; 94-50
ISSN: 1052-5378

                      Biotechnology: Bioremediation
                     Kim Guenther and Raymond Dobert

                       162 citations from AGRICOLA
                         January 1991 - May 1994   

                    Quick bibliography series; 94-50
                               August 1994



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1 NAL Call. No.: QH442.G456 Accessing bioremediation technologies via tech transfer from government & industry.
Day, S.M.
New York, N.Y. : Mary Ann Liebert; 1992 Jun15. Genetic engineering news v. 12 (10): p. 4, 11; 1992 Jun15.

Language: English

Descriptors: Technology transfer; Diffusion of information; Diffusion of research; Technical progress; Biotechnology; Waste treatment; Government research; Research

2 NAL Call. No.: 450 AN7 Acclimation of trees to pollution stress: cellular metal tolerance traits. Dickinson, N.M.; Turner, A.P.; Watmough, S.A.; Lepp, N.W. London : Academic Press; 1992 Dec.
Annals of botany v. 70 (6): p. 569-572; 1992 Dec. Includes references.

Language: English

Descriptors: Uk; Acer pseudoplatanus; Cell suspensions; Shoots; Explants; Air pollution; Copper; Cadmium; Phytotoxicity; Injuries; Acclimatization; Stress response

Abstract: Cell suspension cultures were established from shoot explants of mature trees of Acer pseudoplatanus L. (sycamore) at a site contaminated by aerial deposition of copper and cadmium from metal processing industry, and from the same species at uncontaminated sites. The responses of cell cultures to elevated metal concentrations in growth media differed markedly according to site of origin. Both Cu and Cd, applied singly at concentrations of 10-15 mg l-1 inhibited growth and were toxic to cultures originating from the uncontaminated sites, but not to cultures from the contaminated site. This metal tolerance trait in the cultures from the contaminated site was stable through repeated sub-culturing. It could also be induced in one culture originating from the reference uncontaminated site, by gradually exposing the culture to increasing concentrations of Cu. A reduced level of metal removal from the media was found in tolerant cultures, compared to non-tolerant cultures. The results of these experiments demonstrate the occurrence of an alteration of gene expression in response to pollution stress, suggesting that metal tolerance may be induced within shoot meristems in vivo. It also represents the first example of non-mycorrhizal adaptation to metal toxicity identified in woody plants.

3 NAL Call. No.: QK725.I43 Accumulation of toxic metal ions on cell walls of Datura innoxia suspension cell cultures.
Jackson, P.J.; Anderson, W.L.; DeWitt, J.G.; Ke, H.Y.D.; Kuske, C.R.; Moncrief, R.M.; Rayson, G.D.
Columbia, MD : Tissue Culture Association, c1991-; 1993 Oct. In vitro cellular & developmental biology. Plant : journal of the Tissue Culture Association v. 29P (4): p. 220-226; 1993 Oct. Paper presented at the "Session-in-Depth Bioremediation through Biotechnological Means" at the 1993 Congress on Cell and Tissue Culture, June 5-9, 1993, San Diego, California. Includes references.

Language: English

Descriptors: Datura fastuosa; Metal ions; Adsorption; Cell walls; Cell suspensions; Bioremediation

4 NAL Call. No.: QH442.A1G4 Actinomycetes as agents of biodegradation in the environment--a review. McCarthy, A.J.; Williams, S.T.
Amsterdam : Elsevier Science Publishers; 1992. Gene v. 115 (1/2): p. 189-192; 1992. Paper presented at the "Eighth International Symposium on Biology of Actinomycetes," August 11-16, 1991, Madison, Wisconsin. Literature review. Includes references.

Language: English

Descriptors: Actinomycetales; Soil bacteria; Carbon cycle; Cycling; Microbial degradation; Lignocellulose; Ligninolytic microorganisms; Lignocellulosic wastes; Composting; Recombinant DNA; Literature reviews; Genetic engineering

Abstract: The diversity of form in the Actinomycetales is well-recognised, due to the sustained generation of environmental isolates for pharmaceutical screening. Actinomycetes isolated from soil and related substrates show primary biodegradative activity, secreting a range of extracellular enzymes and exhibiting the capacity to metabolise recalcitrant molecules. Composting is one process which relies heavily on such prolific actinomycete activity. Amongst actinomycetes in soil, there are examples of different strategies, from cycles of rapid proliferation and sporulation to the maintenance of populations by prolonged slow growth and scavenging, and the evidence for this is examined. The mechanisms of lignocellulose degradation by actinomycetes are discussed in relation to functional conservation within the group, and correlations with those described in other bacteria and fungi.

5 NAL Call. No.: QR53.B56 Aerobic metabolism of pentachlorophenol by spent sawdust culture of "Shiitake" mushroom (Lentinus edodes) in soil.
Okeke, B.C.; Smith, J.E.; Paterson, A.; Watson-Craik, I.A. Middlesex : Science and Technology Letters; 1993 Oct. Biotechnology letters v. 15 (10): p. 1077-1080; 1993 Oct. Includes references.

Language: English

Descriptors: Lentinula edodes; Mycelium; Pentachlorophenol; Bioremediation; Soil pollution; Mushroom compost; Hydrogen peroxide

Abstract: Spent sawdust cultures of the Shiitake mushroom (Lentinus edodes) metabolised pentachlorophenol in soil to a significant (P < 0.05) extent with 60.5, 57.3 and 44.4% disappearance recorded for strains LE2, 866 and R26, respectively. Addition of H2O2 markedly enhanced pentachlorophenol metabolism. Analysis of metabolites by GC/MS showed that pentachloroanisole was a metabolic product. These results suggest that there is potential for commercial application in bioremediation.

6 NAL Call. No.: QR97.X46B56 Aerobic, phenol-induced TCE degradation in completely mixed, continuous-culture reactors.
Coyle, C.G.; Parkin, G.F.; Gibson, D.T. Dordrecht, Netherlands ; Boston : Kluwer Academic Publishers, 1990-; 1993. Biodegradation v. 4 (1): p. 59-69; 1993. Special Issue: Substrate Interactions. Includes references.

Language: English

Descriptors: Trichloroethylene; Microbial degradation; Volatile compounds; Drinking water; Groundwater pollution; Pseudomonas putida; Aerobic treatment; Cultures; Bioreactors; Substrates; Glucose; Acetates; Phenol; Bioremediation

7 NAL Call. No.: QH442.G4522 Agri-diagnostics to market biotech-based, fast field analysis system to test for gasoline contamination.
Crouse, G.
Washington, D.C. : King Pub. Group; 1992 Aug25. Biotech daily v. 1 (11): p. 4; 1992 Aug25.

Language: English

Descriptors: Immunoassay; Polluted soils; Polluted water; Biotechnology

8 NAL Call. No.: QD415.A1J62 Anaerobic remediation of dinoseb from contaminated soil: an on-site demonstration--scientific note.
Roberts, D.J.; Kaake, R.H.; Funk, S.B.; Crawford, D.L.; Crawford, R.L. Totowa, N.J. : Humana Press; 1993.
Applied biochemistry and biotechnology v. 39/40: p. 781-789; 1993. Paper presented at the Fourteenth Symposium on Biotechnology for Fuels and Chemicals held May 11-15, 1992, Gathinburg, Tennessee. Includes references.

Language: English

Descriptors: Idaho; Cabt; Dinoseb; Herbicide residues; Polluted soils; Soil pollution; Bioremediation; Anaerobic treatment; Anaerobic conditions; Starch; Nutrient availability; Microbial degradation

9 NAL Call. No.: QD1.A45 Applicability of biological processes for treatment of soils. Eckenfelder, W.W. Jr; Norris, R.D.
Washington, D.C. : The Society; 1993.
ACS Symposium series - American Chemical Society (518): p. 138-158; 1993. In the series analytic: Emerging technologies for hazardous waste management III / edited by D.W. Tedder and F.G. Pohland. Includes references.

Language: English

Descriptors: Waste water treatment; Soil pollution; Biodegradation; Groundwater; Application to land; Bioremediation

Abstract: Biological processes are used to treat excavated soils, saturated and unsaturated soils in situ, and recovered groundwater. Application of these technologies utilizes the experience gained from waste water treatment and various soils and groundwater remediation methods. These processes can incorporate physical removal along with biooxidation. Site conditions and contaminant properties determine which, if any, biological treatment process is appropriate for a given site. This chapter is an introductory summary of these biological processes.

10 NAL Call. No.: TP248.2.B46 Application of oxygen microbubbles for in situ biodegradation of p-xylene-contaminated groundwater in a soil column. Jenkins, K.B.; Michelsen, D.L.; Novak, J.T. New York, N.Y. : American Institute of Chemical Engineers; 1993 Jul. Biotechnology progress v. 9 (4): p. 394-400; 1993 Jul. Includes references.

Language: English

Descriptors: Pseudomonas putida; Bioremediation; Microbial degradation; Xylene; Groundwater pollution; Bioreactors; Soil; Oxygen; Groundwater; Aerobiosis; Ferrous ions

Abstract: In situ biodegradation of p-xylene was studied in a 7-cm (2.75-in.) soil column using oxygen microbubbles to supply the electron acceptor. Pseudomonas putida continuously degraded p-xylene below detectable limits until the oxygen supply was exhausted. Retention time in the biodegradation zone was approximately 45 min. Vent losses claimed 5-10% of the injected oxygen, with 71-82% being utilized. The pressure drops resulting from increased biomass showed a slight increase over the first few days followed by a gradual decline, indicating that the biomass will not plug the soil matrix under the conditions of this test. The addition of ferrous iron in the feed and its subsequent oxidation to ferric hydroxide did not affect biodegradation, nor did it cause appreciable soil plugging. In order to precipitate the ferrous iron before it reached the microbubbles, an air-sparging section was added. This resulted in volatilization of p-xylene with very little ferrous oxidation until the groundwater reached the oxygen microbubbles.

11 NAL Call. No.: TP248.65.E59T47 1991 Applications of controlled pore inert materials as immobilizing surfaces for microbial consortia in wastewater treatment. Portier, R.J.
New York : Plenum Press; 1991.
Applications of enzyme biotechnology / edited by Jeffery W. Kelly and Thomas O. Baldwin. p. 153-163; 1991. (Industry-university cooperative chemistry program symposia). Paper presented at the Texas A&M University IUCCP Ninth Annual Symposium, March 18-21, 1991, College Station, Texas. Includes references.

Language: English

Descriptors: Pseudomonas; Arthrobacter; Aspergillus niger; Biological treatment; Waste water treatment; Microbial degradation; Bioremediation; Aldrin; Malathion; Groundwater pollution; Insecticide residues; Sugar factory waste; Molasses; Factory effluents; Sucrose; Fermentation

12 NAL Call. No.: TP248.65.E59T47 1991 Applications of molecular biology techniques to the remediation of hazardous waste.
Ensley, B.D.
New York : Plenum Press; 1991.
Applications of enzyme biotechnology / edited by Jeffery W. Kelly and Thomas O. Baldwin. p. 181-190; 1991. (Industry-university cooperative chemistry program symposia). Paper presented at the Texas A&M University IUCCP Ninth Annual Symposium, March 18-21, 1991, College Station, Texas. Includes references.

Language: English

Descriptors: Bacteria; Escherichia coli; Metabolic detoxification; Organic compounds; Wastes; Biological treatment; Bioremediation; Molecular biology; Molecular genetics; Recombinant DNA; Genetic engineering; Microbial degradation

13 NAL Call. No.: SB123.57.I55 1992 Bacterial detoxification of mercury in sediment microcosms. Rochelle, P.A.; Olson, B.H.
Braunschweig, Germany : Biologische Bundesanstalt fur Land- und Forstwirtschaft; 1992.
Proceedings of the 2nd International Symposium on the Biosafety Results of Field Tests of Genetically Modified Plants and Microorganisms : May 11-14, 1992, Goslar, Germany : edited by R. Casper and J. Landsmann. p. 149-152; 1992. Includes references.

Language: English

Descriptors: Mercury; Groundwater pollution; Decontamination; Bacteria; Biotechnology

14 NAL Call. No.: S592.7.A1S6 Bacterial transport through homogeneous soil. Gannon, J.T.; Mingelgrin, U.; Alexander, M.; Wagenet, R.J. Exeter : Pergamon Press; 1991.
Soil biology and biochemistry v. 23 (12): p. 1155-1160; 1991. Includes references.

Language: English

Descriptors: Soil bacteria; Introduced species; Strains; Loam soils; Movement in soil; Downward movement; Adsorption; Macropore flow; Soil mechanics; Infiltration; Pore size; Saturated conditions; Spatial distribution; Soil pollution; Groundwater pollution; Microbial degradation; Pollutants; Benzene; Toluene; Chlorinated hydrocarbons

Abstract: The transport of microorganisms in soils is of major importance for bioremediation of subsurface polluted zones and for pollution of groundwater with pathogens. A procedure for evaluating the relative mobility and recovery of bacteria in the soil matrix was developed. In the method devised, movement of bacteria along the walls of the column of soil and channeling were prevented. Changes in population size during the test period were minimal because temperatures of 2-5 degrees C were maintained and predators and parasites were eliminated by 60(Co) irradiation. The 19 strains of bacteria tested had markedly different degrees of transport. From 0.01 to 15% of the added cells passed through a 5-cm long column of Kendaia loam with four pore volumes of water and from 4.3% to essentially all of the added bacteria were recovered. The marked differences in the mobilities of the various bacteria and the high recoveries of most of the isolates suggested that the procedure developed is a useful means for selecting bacteria according to their mobilities in soils, aquifer materials, and other porous media.

15 NAL Call. No.: 381 J8224 Batch cultivation of Methylosinus trichosporium OB3b. I. Production of soluble methane monooxygenase.
Park, S.; Hanna, M.L.; Taylor, R.T.; Droege, M.W. New York, N.Y. : John Wiley & Sons; 1991 Aug05. Biotechnology and bioengineering v. 38 (4): p. 423-433; 1991 Aug05. Includes references.

Language: English

Descriptors: Methanobacterium; Methane; Oxygenases; Biological production; Cell growth; Optimization

Abstract: Methanotrophs have promising applications in bioremediation and in the production of fuel-related chemicals due to their nonspecific enzyme, methane monooxygenase (MMO). The optimal conditions for cell growth and production of the soluble form of MMO (sMMO) were determined from batch cultivations of an obligatory methanotroph, Methylosinus trichosporium OB3b, in shake flasks and a 5-L bioreactor. It was confirmed that a copper deficiency is essential for the formation of the cytoplasmic sMMO. Optimum cell growth without added copper was observed at pH 6.0-70, temperature of 30-34 degrees C, and phosphate concentration of 10-40 mM. in the bioreactor experiments, external CO2 addition eliminated the long lag period observed in the absence of added CuSO4, i.e., prior to the exponential cell growth phase. When methane was continuously supplied, the profile of the cell growth showed two different phases depending on the availability of nitrate, an initial fast exponential growth phase (specific growth rate, micro = 0.08 h-1) and a later slow growth phase (micro = 0.008 h-1). The cell density at the transition from a fast to a slow growth rate was proportional to the initial medium nitrate concentration in the range 5-20 mM and cell yield was estimated to be 7.14 g dry cell wt/g N. Whole-cell sMMO activity remained essentially constant regardless of the growth rate until cell growth stopped. With an initial medium iron concentration below 40 mM, an abrupt decrease in sMMO activity was observed. The lowered sMMO activity could be restored by supplying additional iron to the bioreactor culture. Cell yield on iron was estimated to be 1.3 X 10(3) g dry cell wt/g Fe.

16 NAL Call. No.: QD415.A1J62 Bench scale studies of the soil aeration process for bioremediation of petroleum hydrocarbons.
Hinchee, R.E.; Arthur, M.
Totowa, N.J. : Humana Press; 1991.
Applied biochemistry and biotechnology v. 28/29: p. 901-915; 1991. Includes references.

Language: English

Descriptors: Soil pollution; Hydrocarbons; Petroleum; Bioremediation

17 NAL Call. No.: QH545.A1C7 Beneficial effects of plants in the remediation of soil and groundwater contaminated with organic materials.
Shimp, J.F.; Tracy, J.C.; Davis, L.C.; Lee, E.; Huang, W.; Erickson, L.E.; Schnoor, J.L.
Boca Raton, Fla. : CRC Press; 1993.
Critical reviews in environmental science and technology v. 23 (1): p. 41-77; 1993. Includes references.

Language: English

Descriptors: Plants; Bioremediation; Polluted soils; Soil pollution; Groundwater pollution; Polluted water; Pollutants; Biodegradation; Microbial degradation; Soil flora; Rhizosphere; Literature reviews

18 NAL Call. No.: QH545.A1E52 Biodegradation of benzene, toluene, ethylbenzene and xylenes in gas-condensate-contaminated ground-water. Morgan, P.; Lewis, S.T.; Watkinson, R.J. Essex : Elsevier Applied Science; 1993. Environmental pollution v. 82 (2): p. 181-190; 1993. Includes references.

Language: English

Descriptors: Netherlands; Groundwater pollution; Benzene; Toluene; Xylene; Aromatic hydrocarbons; Biodegradation; Temperature; Organic matter; Inorganic compounds; Dissolved oxygen; Anaerobic conditions; Microbial activities; Bioremediation

19 NAL Call. No.: QR1.F44 Biodegradation of phenanthrene in soil microcosms stimulated by an introduced Alcaligenes sp.
Moller, J.; Ingvorsen, H.
Amsterdam : Elsevier Science Publishers; 1993 Apr. FEMS microbiology letters - Federation of European Microbiological Societies v. 102 (3/4): p. 271-278; 1993 Apr. Includes references.

Language: English

Descriptors: Alcaligenes; Phenanthrene; Soil pollution; Soil inoculation; Inoculum density; Moisture content; Microbial degradation; Bioremediation

Abstract: A phenanthrene degrading strain of Alcaligenes sp. was isolated from oil polluted soil. Addition of Alcaligenes sp. to soil microcosms supplemented with phenanthrene (1 mg/g dry soil) resulted in degradation of the added phenanthrene within 11 days. The phenanthrene concentration declined only 12% in uninoculated soil during 42 days. The total phenanthrene degradation potential of Alcaligenes sp. was 2.3 mg/g dry soil during a period of 22 days. The amount of CO2 evolved during 22 days corresponded to the conversion of 91% of the degraded phenanthrene to CO2. The Alcaligenes sp. were not able to degrade phenanthrene in sterile soil. Polycyclic aromatic hydrocarbons (PAHs) are hazardous components of hydrocarbon mixtures such as creosote and oil refinery waste, and are common pollution factors in soils and ground waters. Although some decline in PAH content in soil due to abiotic processes has been reported, most of the PAH degradation observed in polluted soils are accomplished by the microbial populations. The effects on the microbial degradation of PAHs in soils by such factors as temperature, fertilization and sorption of the PABs to the soil have been investigated. An approach towards bioremediation of PAH contaminated soil with positive results is the combining of agricultural techniques such as tilling, irrigation and fertilization collectively known as landfarming, although higher molecular weight PAHs tend to persist in the soil.

20 NAL Call. No.: QH540.M64 Biodegradation of phenoxyacetic acid in soil by Pseudomonas putida PP0301 (pR0103), a constitutive degrader of 2,4-dichlorophenoxyacetate. Short, K.A.; King, R.J.; Seidler, R.J.; Olsen, R.H. Oxford : Blackwell Scientific Publications; 1992 Aug. Molecular ecology v. 1 (2): p. 89-94; 1992 Aug. Includes references.

Language: English

Descriptors: Pseudomonas putida; Genetic engineering; 2,4-d; Aromatic acids; Microbial degradation; Herbicide residues; Introduced species; Agricultural soils; Polluted soils; Soil pollution; Recombination

21 NAL Call. No.: 448.3 AP5 Biodegradation of polycyclic aromatic hydrocarbons by new isolates of white rot fungi.
Field, J.A.; Jong, E. de; Costa, G.F.; Bont, J.A.M. de Washington, D.C. : American Society for Microbiology; 1992 Jul. Applied and environmental microbiology v. 58 (7): p. 2219-2226; 1992 Jul. Includes references.

Language: English

Descriptors: Decay fungi; Strains; Phanerochaete chrysosporium; Coriolus versicolor; Bjerkandera adusta; Polyporus; Microbial degradation; Polycyclic hydrocarbons; Aromatic hydrocarbons; Pollutants; Soil pollution; Sediment; Ligninolytic microorganisms

Abstract: Eight rapid Poly R-478 dye-decolorizing isolates from The Netherlands were screened in this study for the biodegradation of polycyclic aromatic hydrocarbons (PAH) supplied at 10 mg liter-1. Several well-known ligninolytic culture collection strains, Phanerochaete chrysosporium BKM-F-1767, Trametes versicolor Paprican 52, and Bjerkandera adusta CBS 595.78 were tested in parallel. All of the strains significantly removed anthracene, and nine of the strains significantly removed benzo[a]pyrene beyond the limited losses observed in sterile liquid and HgCl2-poisoned fungus controls. One of the new isolates, Bjerkandera sp. strain Bos 55, was the best degrader of both anthracene and benzo[a]pyrene, removing 99.2 and 83.1% of these compounds after 28 days, respectively. Half of the strains, exemplified by strains of the genera Bjerkandera and Phanerochaete, converted anthracene to anthraquinone, which was found to be a dead-end metabolite, in high yields. The extracellular fluids of selected strains were shown to be implicated in this conversion. In contrast, four Trametes strains removed anthracene without significant accumulation of the quinone. The ability of Trametes strains to degrade anthraquinone was confirmed in this study. None of the strains accumulated PAH quinones during benzo[a]pyrene degradation. Biodegradation of PAH by the various strains was highly correlated to the rate by which they decolorized Poly R-478 dye, demonstrating that ligninolytic indicators are useful in screening for promising PAH-degrading white rot fungal strains.

22 NAL Call. No.: TP995.A1I5 Biological treatment of groundwater, soils, and soil vapors contaminated with petroleum hydrocarbons.
Galaska, E.G.; Skladany, G.J.; Nyer, E.K. Chelsea, Mich. : Lewis Publishers; 1990. Proceedings of the Industrial Waste Conference, Purdue University (44th): p. 11-21; 1990. Meeting held on May 9-11, 1989, Purdue University, West Lafayette, Indiana. Includes references.

Language: English

Descriptors: Soil pollution; Polluted soils; Petroleum; Petroleum hydrocarbons; Contamination; Biological treatment; Microbial degradation; Soil air; Biological fixed-film systems; Bacteria; Groundwater pollution; Benzene; Toluene; Xylene; Bioreactors

23 NAL Call. No.: QD415.A1J62 Bioremediating herbicide-contaminated soils. Dzantor, E.K.; Felsot, A.S.; Beck, M.J. Totowa, N.J. : Humana Press; 1993.
Applied biochemistry and biotechnology v. 39/40: p. 621-630; 1993. Paper presented at the Fourteenth Symposium on Biotechnology for Fuels and Chemicals held May 11-15, 1992, Gathinburg, Tennessee. Includes references.

Language: English

Descriptors: Alachlor; Atrazine; Metolachlor; Trifluralin; Herbicide residues; Soil pollution; Polluted soils; Bioremediation; Microbial degradation; Soil flora; Application to land

24 NAL Call. No.: TA166.T72 Bioremediation: a response to gross environmental abuse. Hamer, G.
Cambridge : Elsevier Science Publishing Co; 1993 Aug. Trends in biotechnology v. 11 (8): p. 317-319; 1993 Aug. In the special issue: Bioremediation: technological and commercial issues in the biological detoxification of polluted sites.

Language: English

Descriptors: Industrial wastes; Pollution control; Bioremediation

25 NAL Call. No.: QR1.F4 Bioremediation and waste management.
Bewley, R.J.F.
Madison, Wis. : Science Tech Publishers; 1992. FEMS symposium - Federation of European Microbiological Societies (63): p. 33-45; 1992. In the series analytic: The release of genetically modified microorganisms--REGEM 2 / edited by D.E.S. Stewart-Tull and M. Sussman. Paper presented at the "Symposium on the Release of Genetically Modified Microorganisms--REGEM 2," August 29-31, 1991, Nottingham, UK. Includes references.

Language: English

Descriptors: Microorganisms; Pseudomonas putida; Pseudomonas fluorescens; Phanerochaete chrysosporium; Anaerobes; Genetic engineering; Pollutants; Microbial degradation; Bioremediation; Polluted soils; Soil pollution; Soil inoculation

26 NAL Call. No.: GC1085.B55 Bioremediation for marine oil spills.
United States, Congress, Office of Technology Assessment Washington, D.C. : Congress of the U.S., Office of Technology Assessment : For sale by the Supt. of Docs., U.S. G.P.O.,; 1991; Y 3.T 22/2:2 B 52/7. v, 31 p. : ill. ; 26 cm. (Background paper). "May 1991"--P. [4] of cover. "OTA-BP-O-70"--P. [4] of cover. Includes bibliographical references.

Language: English; English

Descriptors: Oil spills; Oil pollution of the sea; Environmental biotechnology; Environmental protection

27 NAL Call. No.: TD420.A1E5 Bioremediation in the rhizosphere.
Anderson, T.A.; Guthrie, E.A.; Walton, B.T. Washington, D.C. : American Chemical Society; 1993 Dec. Environmental science & technology v. 27 (13): p. 2630-2637; 1993 Dec. Includes references.

Language: English

Descriptors: Soil pollution; Organic compounds; Rhizosphere; Bioremediation; Microbial degradation

28 NAL Call. No.: TP995.A1I5 Bioremediation of ethanol and petroleum hydrocarbon contaminated groundwater using a rotating biological contactor.
Engelder, C.L.; Matson, S.A.
Chelsea, Mich. : Lewis Publishers; 1991. Proceedings of the Industrial Waste Conference, Purdue University (45th): p. 287-294; 1991. Meeting held on May 8-10, 1990, Purdue University, West Lafayette, Indiana. Includes references.

Language: English

Descriptors: Groundwater pollution; Ethanol; Petroleum hydrocarbons; Groundwater; Water purification; Biological treatment; Rotating biological contactors

29 NAL Call. No.: TP995.A1I5 Bioremediation of former manufactured gas plant sites. Srivastava, V.J.; Kilbane, J.J.; Kelley, R.L.; Gauger, W.K.; Akin, C.; Hayes, T.D.; Linz, D.G.
Chelsea, Mich. : Lewis Publishers; 1990. Proceedings of the Industrial Waste Conference, Purdue University (44th): p. 49-60; 1990. Meeting held on May 9-11, 1989, Purdue University, West Lafayette, Indiana. Includes references.

Language: English

Descriptors: Soil pollution; Polluted soils; Industrial sites; Town gas; Gas production; Polycyclic hydrocarbons; Aromatic hydrocarbons; Microbial degradation; Biological treatment; Soil bacteria; Reclamation

30 NAL Call. No.: TD1040.B5 Bioremediation of hazardous wastes.
Biosystems Technology Development Program, United States, Environmental Protection Agency
Ada, OK : U.S. Environmental Protection Agency,; 1990. vi, 58 p. : ill. ; 28 cm. Dec. 1990. EPA/600/9-90/041. Includes bibliographical references.

Language: English

Descriptors: Hazardous wastes; Environmental biotechnology

31 NAL Call. No.: TA166.T72 Bioremediation of organic compounds--putting microbial metabolism to work. Bouwer, E.J.; Zehnder, A.J.B.
Cambridge : Elsevier Science Publishing Co; 1993 Aug. Trends in biotechnology v. 11 (8): p. 360-367; 1993 Aug. In the special issue: Bioremediation: technological and commercial issues in the biological detoxification of polluted sites. Includes references.

Language: English

Descriptors: Soil pollution; Groundwater pollution; Pollutants; Organic compounds; Pollution control; Microbial degradation; Bioremediation

Abstract: Microorganisms can metabolize many aliphatic and aromatic organic contaminants, either to obtain carbon and/or energy for growth, or as co-substrates, thus converting them to products such as carbon dioxide, water, chloride and biomass. These biotransformations can be exploited for treatment of contaminated soils and ground water.

32 NAL Call. No.: TD420.A1P7 Bioremediation of PAH-contaminated soil via in-vessel composting. Adenuga, A.O.; Johnson, J.H. Jr; Cannon, J.N.; Wan, L. Oxford : Pergamon Press; 1992.
Water science and technology : a journal of the International Association on Water Pollution Research and Control v. 26 (9/11): p. 2331-2334; 1992. In the series analytic: Water Quality International '92. Part 5 / edited by M. Suzuki, et.al. Proceedings of the Sixteenth Biennial Conference of the International Association on Water Pollution Research and Control held May 24-30, 1992, Washington, D.C. Includes references.

Language: English

Descriptors: Soil pollution; Pollutants; Polycyclic hydrocarbons; Aromatic hydrocarbons; Biodegradation; Composting

33 NAL Call. No.: TD879.P4R57 1992 Bioremediation of petroleum contaminated sites. Riser-Roberts, Eve
Chelsea, Mich. : C.K. Smoley,; 1992.
1 v. (various pagings) : ill., map ; 25 cm. Includes bibliographical references and index.

Language: English

Descriptors: Oil pollution of soils; Oil pollution of water; Petroleum; Bioremediation

34 NAL Call. No.: TD172.J6 Bioremediation of petroleum contaminated soil using vegetation: a microbial study.
Lee, E.; Banks, M.K.
New York, Marcel Dekker; 1993.
Journal of environmental science and health: Part A: Environmental science and engineering v. A28 (10): p. 2187-2198; 1993. Includes references.

Language: English

Descriptors: Polluted soils; Petroleum; Contaminants; Pollutants; Rhizosphere; Microbial degradation; Microorganisms; Population density; Biological activity in soil; Bioremediation; Medicago sativa

35 NAL Call. No.: QH545.A1E52 Bioremediation of soil contaminated with polynuclear aromatic hydrocarbons (PAHs): a review.
Wilson, S.C.; Jones, K.C.
Essex : Elsevier Applied Science; 1993. Environmental pollution v. 81 (3): p. 229-249; 1993. Literature review. Includes references.

Language: English

Descriptors: Aromatic hydrocarbons; Contaminants; Bioremediation; Polluted soils; Literature reviews

36 NAL Call. No.: 500 N484 Bioremediation of soils contaminated with pentachlorophenol. Bajpai, R.; Banerji, S.
New York, N.Y. : The Academy; 1992.
Annals of the New York Academy of Sciences v. 665: p. 423-434; 1992. In the analytic series: Biochemical engineering VII / edited by H. Pedersen, R. Mutharasan, and D. DiBiasio. Includes references.

Language: English

Descriptors: Pentachlorophenol; Pesticide residues; Soil pollution; Biodegradation; Decontamination; Microorganisms; Photolysis

37 NAL Call. No.: S590.A48 Bioremediation of soils contaminated with selenium. Thompson-Eagle, E.T.; Frankenberger, W.T. Jr New York, N.Y. : Springer-Verlag; 1992. Advances in soil sciences. p. 261-310; 1992. In the series analytic: Soil restoration / edited by R. Lal and B.A. Stewart. Includes references.

Language: English

Descriptors: California; Agricultural soils; Soil pollution; Contamination; Selenium; Cycling; Nutrient uptake; Transformation; Soil flora; Reclamation; Losses from soil systems

38 NAL Call. No.: TD192.5.B58 The Bioremediation report.
COGNIS, Inc, King Communications Group Inc Santa Rosa, CA : COGNIS, Inc.,; 1991-9999. The Bioremediation report. v. : ill. ; 28 cm; 1991-9999. Description based on: Vol. 1, no. 6 (June 1992); title from caption. Vols. for <-Sept. 1992> issued by COGNIS, Inc.; <Apr. 1993-> by King Communications Group, Inc.

Language: English

Descriptors: Bioremediation

39 NAL Call. No.: QH540.S8 no.51 Biotechniques for air pollution abatement and odour control policies proceedings of an international symposium, Maastricht, the Netherlands, 27-29 October, 1991.
Dragt, A. J.; Ham, J. van
Vereniging Lucht (Netherlands)
Amsterdam ; New York : Elsevier,; 1992. xv, 457 p. : ill., maps ; 25 cm. (Studies in environmental science ; 51). English and German. Society for Clean Air in the Netherlands, Vereniging Lucht. Includes bibliographical references and indexes.

Language: English; German

Descriptors: Air quality management; Odor control; Bioremediation

40 NAL Call. No.: TP248.3.A38 Biotechnological reduction of CO2 emissions. Karube, I.; Takeuchi, T.; Barnes, D.J.
Berlin, W. Ger. : Springer-Verlag; 1992. Advances in biochemical engineering/biotechnology (46): p. 63-79; 1992. In the series analytic: Modern biochemical engineering / edited by T. Scheper. Literature review. Includes references.

Language: English

Descriptors: Algae; Photosynthesis; Carbon dioxide; Bioreactors; Air pollution; Biological treatment; Factory fumes; Literature reviews

Abstract: Biotechnological fixation of carbon dioxide (CO2) is described as a measure for reducing CO2 emissions. Photosynthesis by microalgae would provide an efficient mechanism for the reduction of CO2, if well-designed photobioreactors could be constructed for the intensive cultivations. Screening of microalgae which can grow well under high CO2 concentrations would also be necessary in order to establish biotechnological CO2 reduction systems. In addition, calcification and vegetation are discussed as mechanisms for reducing CO2 emissions. Environmental monitoring is significantly important for the understanding of global CO2 cycle, so that recent development in sensor technology are also described.

41 NAL Call. No.: 449.9 V58 Bd.80 Biotechnologische In-situ-Sanierung kontaminierter Standorte internationales Fachgesprach in Langen, 11. und 12. Mai 1987 [Biotechnological in situ rehabilitation of contaminated sites].
Filip, Zdenek,
Stuttgart ; New York : G. Fischer,; 1988. 394 p. ; 21 cm. (Schriftenreihe des Vereins fur Wasser-, Boden- und Lufthygiene ; 80). Contributions in German and English. Includes bibliographical references.

Language: German; English

Descriptors: Soil pollution; Water, Underground; Environmental biotechnology

42 NAL Call. No.: TD192.5.B56 Biotechnology and biodegradation.
Kamely, Daphne; Chakrabarty, Ananda M.,_1938-; Omenn, Gilbert S. International Workshop on Biotechnology and Biodegradation 1989 : Lisbon, Portugal.
Woodlands, Tex. : Portfolio Pub. Co. ; Houston : Gulf Pub. Co.,; 1990. xxiii, 504 p. : ill. ; 24 cm. (Advances in applied biotechnology series ; v. 4). Papers presented at the International Workshop on Biotechnology and Biodegradation, held in Lisbon, Portugal, June 1989. Includes bibliographical references and index.

Language: English

Descriptors: Bioremediation; Biodegradation

43 NAL Call. No.: TP248.14.B5592 1993 Biotechnology and environmental science molecular approaches. Mongkolsuk, S.; Lovett, P. S.; Trempy, J. New York : Plenum Press,; 1993.
p. cm. "Proceedings of an international conference on biotechnology and environmental science: molecular approaches, held August 21-24, 1990, in Bangkok, Thailand"--T.p. verso. Includes bibliographical references and index.

Language: English

Descriptors: Biotechnology; Bioremediation; Agricultural biotechnology; Microbial biotechnology

44 NAL Call. No.: QH540.J6 Biotechnology and hazardous waste treatment. Stroo, H.F.
Madison, Wis. : American Society of Agronomy; 1992 Apr. Journal of environmental quality v. 21 (2): p. 167-175; 1992 Apr. Includes references.

Language: English

Descriptors: Pesticides; Industrial wastes; Biological treatment; Biotechnology; Fungi; Microbial degradation

Abstract: Despite considerable speculation and research on the potential for biotechnology to improve the treatment of hazardous wastes, little progress has been made to date in developing commercially available products and processes. This paper examines the current state of the art and the progress to date, as well as the barriers to biotechnological advances in hazardous waste treatment. The potential applications of biotechnology are also discussed, in terms of the contaminated matrix, the type of reactor technology used and the types of compounds present. The most promising areas for technology development efforts are identified, as well as the critical issues which must be addressed in moving from laboratory-scale testing to the development of commercially-viable technologies.

45 NAL Call. No.: aZ5071.N3 Biotechnology: bioremediation: January 1987-March 1992. Warmbrodt, R.D.; Wiggert, L.
Beltsville, Md. : The Library; 1992 May. Quick bibliography series - U.S. Department of Agriculture, National Agricultural Library (U.S.). (92-47): 44 p.; 1992 May. Updates QB 91-106. Bibliography.

Language: English

Descriptors: Environment; Genetic engineering; Biotechnology; Bibliographies

46 NAL Call. No.: QD1.A45 Biotechnology in bioremediation of pesticide-contaminated sites. Karns, J.S.
Washington, D.C. : American Chemical Society, 1974-; 1992. ACS symposium series (510): p. 148-156; 1992. In the series analytic: Pesticide Waste Management: technology and regulation / edited by J.B. Bourke, A.S. Felsot, T.J. Gilding, J.K. Jensen, J.N. Seiber. Includes references.

Language: English

Descriptors: Pesticides; Contamination; Waste disposal sites; Bioremediation; Biotechnology; Microbial degradation; Waste treatment

47 NAL Call. No.: S494.5.B563B57 Biotechnology in pesticide environmental research. Karns, J.S.; Mulbry, W.W.; Kearney, P.C. Boston : Kluwer Academic Publishers; 1986. Biotechnology for solving agricultural problems : invited papers presented at a symposium held May 5-9, 1985, at the Beltsville Agricultural Research Center, Beltsville, Maryland. p. 339-354; 1986. (Beltsville symposia in agricultural research : 10 ;). Includes references.

Language: English

Descriptors: Flavobacterium; Gracilicutes; Coumaphos; Carbofuran; Microbial degradation

48 NAL Call. No.: QR97.X46B56 Biotechnology in the degradation and utilization of lignocellulose. Broda, P.
Dordrecht, The Netherlands. : Kluwer Academic Publishers; 1992. Biodegradation v. 3 (2/3): p. 219-238; 1992. In the Special Issue: Microorganisms to Combat Pollution / edited by E. Rosenberg. Paper presented at an International Workshop on the "Use of Microorganisms to Combat Pollution," May 10-18, 1992, Israel. Includes references.

Language: English

Descriptors: Lignocellulose; Cellulose; Enzymes; Biodegradation; Phanerochaete chrysosporium; Streptomyces; Gene expression; Lignin; Biotechnology; Wastage; Waste utilization

49 NAL Call. No.: A00040 Biotechnology's coming of age.
Dutton, G.
New York, N.Y. : Schnell Pub. Co. :.; 1992 May. Chemical business v. 14 (5): p. 19-21; 1992 May.

Language: English

Descriptors: Lycopersicon esculentum; Genetic engineering; Pest resistance; Crops; Bacillus thuringiensis; Product development; Pesticides; Biodegradation

50 NAL Call. No.: QR53.J68 Bioventing soils contaminated with petroleum hydrocarbons. Hoeppel, R.E.; Hinchee, R.E.; Arthur, M.F. Amsterdam : Elsevier Science Publishers on behalf of the Society for Industrial Microbiology; 1991 Oct.
Journal of industrial microbiology v. 8 (3): p. 141-146; 1991 Oct. Includes references.

Language: English

Descriptors: Soil pollution; Petroleum hydrocarbons; Microbial degradation

Abstract: Bioventing combines the capabilities of soil venting and enhanced bioremediation to cost-effectively remove light and middle distillate hydrocarbons from vadose zone soils and the groundwater table. Soil venting removes the more volatile fuel components from unsaturated soil and promotes aerobic biodegradation by driving large volumes of air into the subsurface. In theory, air is several thousand times more effective than water in penetrating and aerating fuel-saturated and low permeability soil horizons. Aerobic microbial degradation can mitigate both residual and vapor phase hydrocarbon concentrations. Soil venting is being evaluated at a number of U.S. military sites contaminated with middle distillate fuels to determine its potential to stimulate in situ aerobic biodegradation and to develop techniques to promote in situ vapor phase degradation. In situ respirometric evaluations and field pilot studies at sites with varying soil conditions indicate that bioventing is a cost-effective method to treat soils contaminated with jet fuels and diesel.

51 NAL Call. No.: QD415.A1J62 Carbon dioxide fixation by microalgae photosynthesis using actual flue gas discharged from a boiler.
Negoro, M.; Hamasaki, A.; Ikuta, Y.; Makita, T.; Hirayama, K.; Suzuki, S. Totowa, N.J. : Humana Press; 1993.
Applied biochemistry and biotechnology v. 39/40: p. 643-653; 1993. Paper presented at the Fourteenth Symposium on Biotechnology for Fuels and Chemicals held May 11-15, 1992, Gathinburg, Tennessee. Includes references.

Language: English

Descriptors: Chlorophyta; Bacillariophyta; Photosynthesis; Carbon dioxide; Biological treatment; Exhaust gases; Power industry

52 NAL Call. No.: QH442.J69 Cartapip: a biopulping product for control of pitch and resin acid problems in pulp mills.
Farrell, R.L.; Blanchette, R.A.; Brush, T.S.; Hadar, Y.; Iverson, S.; Krisa, K.; Wendler, P.A.; Zimmerman, W.
Amsterdam : Elsevier Science Publishers B.V.; 1993 Jul. Journal of Biotechnology v. 30 (1): p. 115-122; 1993 Jul. In the special issue: Lignin biodegradation and practical utilization / edited by C.V. Bruschi. Proceedings of the ICGEB Colloquium, June 27-30, 1990, Trieste, Italy. Includes references.

Language: English

Descriptors: Ophiostoma; Pitch; Resins; Microbial degradation; Industrial microbiology; Biotechnology; Wood chips; Blue stain; Biological competition; Wood pulp; Bleaching

53 NAL Call. No.: 448.3 J82 Characterization of a flavobacterium glutathione S-transferase gene involved in reductive dechlorination.
Orser, C.S.; Dutton, J.; Lange, C.; Jablonski, P.; Xun, L.; Hargis, M. Washington, D.C. : American Society for Microbiology; 1993 May. Journal of bacteriology v. 175 (9): p. 2640-2644; 1993 May. Includes references.

Language: English

Descriptors: Flavobacterium; Structural genes; Lyases; Glutathione transferase; Nucleotide sequences; Amino acid sequences; Enzyme activity; Organochlorine compounds; Pentachlorophenol; Chemical reactions; Bioremediation; Microbial degradation; Soil pollution

Abstract: The gene pcpC, encoding tetrachloro-p-hydroquinone (TeCH) reductive dehalogenase, was cloned from Flavobacterium sp. strain ATCC 39723 and sequenced. The gene was identified by hybridization with a degenerate oligonucleotide designed from the N-terminal sequence of the purified protein. An open reading frame of 747 nucleotides was found, which predicts a translational product of 248 amino acids having a molecular weight of 28,263, which agrees favorably with the sodium dodecyl sulfate-polyacrylamide gel electrophoresis-determined molecular weight of 30,000 reported for the purified protein. The predicted translational product of pcpC matched the N-terminal sequence of the purified protein exactly. From the nucleotide sequence, the protein appears to have a processed formylmethionyl. An Escherichia coli pcpC overexpression clone was shown to produce dichlorohydroquinone and trichlorohydroquinone from TeCH. Protein data base searches grouped the predicted translational sequence of pcpC with two previously reported plant glutathione S-transferases but less significantly with any of the mammalian glutathione S-transferases or the glutathione-utilizing, hydrolytic dechlorinating enzyme from Methylobacterium sp. strain DM4.

54 NAL Call. No.: QH545.A1E58 Chemical and toxicological testing of composted explosives-contaminated soil. Griest, W.H.; Stewart, A.J.; Tyndall, R.L.; Caton, J.E.; Ho, C.H.; Ironside, K.S.; Caldwell, W.M.; Tan, E.
Tarrytown, N.Y. : Pergamon Press; 1993 Jun. Environmental toxicology and chemistry v. 12 (6): p. 1105-1116; 1993 Jun. Includes references.

Language: English

Descriptors: Polluted soils; Explosives; Composting; Bioremediation; Ceriodaphnia dubia; Mortality; Mutagenicity; Military areas

55 NAL Call. No.: QD415.A1J62 Chemical interaction of flue gas components with the growth of Cyanidium caldarium: scientific note.
Woodward, C.A.; MacInnis, J.M.; Lewis, S.N.; Greenbaum, E. Totowa, N.J. : Humana Press; 1992.
Applied biochemistry and biotechnology v. 34/35: p. 819-826; 1992. Paper presented at the "Thirteenth Symposium on Biotechnology for Fuels and Chemicals," May 6-10, 1991, Colorado Springs, Colorado. Includes references.

Language: English

Descriptors: Algae; Exhaust gases; Biological treatment; Carbon dioxide; Photosynthesis; Oxygen; Gas production; Bioreactors; Air pollution

56 NAL Call. No.: S612.A753 Cleopatra's bathwater: an informal introduction to the art and science of bioremediation.
Ausubel, K.
Tucson, Ariz. : Office of Arid Lands Studies, University of Arizona; 1992. Arid lands newsletter v. 32: p. 2-4; 1992.

Language: English

Descriptors: Arizona; Biotechnology; Water resources; Wetlands; Waste water treatment; Marshes

57 NAL Call. No.: 448.3 J82 Cloning, sequence analysis, and expression of the Flavobacterium pentachlorophenol-4-monooxygenase gene in Escherichia coli. Orser, C.S.; Lange, C.C.; Xun, L.; Zahrt, T.C.; Schneider, B.J. Washington, D.C. : American Society for Microbiology; 1993 Jan. Journal of bacteriology v. 175 (2): p. 411-416; 1993 Jan. Includes references.

Language: English

Descriptors: Flavobacterium; Structural genes; Oxygenases; Cloning; Nucleotide sequences; Amino acid sequences; Gene expression; Genetic transformation; Escherichia coli; Pentachlorophenol; Microbial degradation; Enzyme activity; Chemical reactions

Abstract: The pcpB gene of Flavobacterium sp. strain ATCC 39723 was cloned by using a degenerate primer designed from the N-terminal sequence of the purified enzyme. The nucleotide sequence of pcpB was determined and found to encode an open reading frame of 1,614 nucleotides, yielding a predicted translation product of 538 amino acids, in agreement with the estimated size of the purified protein analyzed by sodium dodecyl sulfate-polyacrylamide gel electrophoresis. The transcriptional start of pcpB was found to be 80 bp upstream of the translational start, and the transcript was found to be induced in Flavobacterium sp. strain ATCC 39723 by the presence of pentachlorophenol but to be constitutive in the Escherichia coli pcpB clone. DNA hybridizations with genomic DNAs from Arthrobacter sp. strain ATCC 33790 and Pseudomonas sp. strain SR3 revealed a similar-size 3.0-kb EcoRI fragment, whereas there was no positive hybridization with genomic DNA from Rhodococcus chlorophenolicus. Cell extracts from an E. coli pcpB overexpression strain, as well as the whole cells, were proficient in the dechlorination of pentachlorophenol to tetrachlorohydroquinone. Protein data base comparisons of the predicted translation products revealed regions of homology with other microbial monooxygenases, including phenol-2-monooxygenase and tryptophan-2-monooxygenase.

58 NAL Call. No.: 300.9 Am3 Colley lecture: new technology to remediate wood treating sites. McGinnis, G.
Stevensville, Md. : The Association; 1993. Proceedings, ... annual meeting of the American Wood-Preservers' Association v. 88: p. 16-19; 1993. Meeting held May 17-20, 1992, Washington, D.C.

Language: English

Descriptors: U.S.A.; Cabt; Soil pollution; Groundwater pollution; Bioremediation; Wood; Treatment

59 NAL Call. No.: QR1.F4 Commercial use of microbial inocula containing live genetically modified microorganisms (GEMMOs).
Harris, W.J.
Madison, Wis. : Science Tech Publishers; 1992. FEMS symposium - Federation of European Microbiological Societies (63): p. 85-92; 1992. In the series analytic: The release of genetically modified microorganisms--REGEM 2 / edited by D.E.S. Stewart-Tull and M. Sussman. Paper presented at the "Symposium on the Release of Genetically Modified Microorganisms--REGEM 2," August 29-31, 1991, Nottingham, UK. Includes references.

Language: English

Descriptors: Microorganisms; Genetic engineering; Inoculum; Introduced species; Economic evaluation; Production economics; Microbial degradation; Pollutants; Bioremediation; Polluted soils; Microbial pesticides

60 NAL Call. No.: QD1.A45 Comparison of the effectiveness of emerging in situ technologies and traditional ex situ treatment of solvent-contaminated soils. Just, S.R.; Stockwell, K.J.
Washington, D.C. : The Society; 1993.
ACS Symposium series - American Chemical Society (518): p. 238-277; 1993. In the series analytic: Emerging technologies for hazardous waste management III / edited by D.W. Tedder and F.G. Pohland. Includes references.

Language: English

Descriptors: Soil pollution; Waste disposal; Solvents; Technology; Heat treatment; Extraction; Biodegradation; Flushing; Washing; Comparisons

Abstract: This chapter examines the applicability of various treatment technologies to the remediation of contaminated soils in light of the Land Disposal Restrictions (LDRs) which were fully implemented for F001-F005 solvent contaminated wastes in November of 1990. Both traditional and emerging technologies are reviewed, including low temperature thermal treatment, radio frequency heating, steam stripping, vacuum extraction, aeration, in-situ bioremediation, and soil flushing/washing. In discussing the applicability of each technology, the feasibility, advantages, disadvantages, limitations, and performance of the treatment methods are reviewed. The treatment of soil contaminated with spent solvents such as trichloroethylene (TCE) is emphasized, and cleanup levels achieved during studies of different technologies are discussed. For some technologies, information concerning solvent removal was limited, and the treatment of other contaminants is summarized. The chapter concludes with a comparison of the removal efficiencies attained through emerging in-situ technologies and more traditional ex-situ treatment.

61 NAL Call. No.: QR53.J68 Composting of explosives and propellant contaminated soils under thermophilic and mesophilic conditions.
Williams, R.T.; Ziegenfuss, P.S.; Sisk, W.E. Amsterdam, The Netherlands : Published by Elsevier Science Publishers on behalf of the Society for Industrial Microbiology, c1986-; 1992 Feb. Journal of industrial microbiology v. 9 (2): p. 137-144; 1992 Feb. Includes references.

Language: English

Descriptors: Soil pollution; Explosives; Contaminants; Composting; Bioremediation

Abstract: Composting was investigated as a bioremediation technology for clean-up of sediments contaminated with explosives and propellants. Two field demonstrations were conducted, the first using 2,4,6-trinitrotoluene (TNT), octahydro-1;3,5,7-tetranitro-1,3,5,7-tetraazocine (HMX), hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX), and N-methyl-N,2,4,6-tetranitroaniline (tetryl) contaminated sediment, and the second using nitrocellulose (NC) contaminated soil. Tests were conducted in thermophilic and mesophilic aerated static piles. Extractable TNT was reduced from 11840 mg/kg to 3 mg/kg, and NC from 13090 mg/kg to 16 mg/kg under thermophilic conditions. Under mesophilic conditions, TNT was reduced from 11 190 mg/kg to 50 mg/kg. The thermophilic and mesophilic half-lives were 11.9 and 21.9 days for TNT, 17.3 and 30.1 days for RDX, and 22.8 and 42.0 days for HMX, respectively. Known nitroaromatic transformation products increased in concentration over the first several weeks of the test period, but decreased to low concentrations thereafter.

62 NAL Call. No.: GB651.N3 Conserving microbial gene pools for sustainable development. Stevenson, R.E.
Paris : Unesco; 1991.
Nature and resources v. 27 (3): p. 37-42; 1991. Includes references.

Language: English

Descriptors: Biotechnology; Sustainability; Microorganisms; Genetic resources; Culture collections; Cultures; Preservation; Microbial degradation; Biological treatment; Wastes; Technology transfer; International cooperation

63 NAL Call. No.: 448.3 AP5 Construction and characterization of heavy metal-resistant haloaromatic-degrading Alcaligenes eutrophus strains. Springael, D.; Diels, L.; Hooyberghs, L.; Kreps, S.; Mergeay, M. Washington, D.C. : American Society for Microbiology; 1993 Jan. Applied and environmental microbiology v. 59 (1): p. 334-339; 1993 Jan. Includes references.

Language: English

Descriptors: Alcaligenes; Metal tolerance; Heavy metals; Microbial degradation; 2,4-d; Polychlorinated biphenyls; Bioremediation; Genetic engineering; Plasmids; Genetic transformation

Abstract: Alcaligenes eutrophus strains exhibiting both plasmid-borne heavy metal resistance and haloaromatic-degrading functions were obtained by intraspecific conjugation. The strains which we constructed expressed catabolic and resistance markers together. Degradation of various polychlorinated biphenyl isomers and 2,4-D (2,4-dichlorophenoxyacetic acid) was observed in the presence of 1 mM nickel or 2 mM zinc, provided that the metal resistance determinant was present in the catabolizing strain. Such strains may be useful for decontamination of sites that are polluted with both organic compounds and heavy metals.

64 NAL Call. No.: TD879.P4C66 1992 Contaminated soils diesel fuel contamination. Kostecki, Paul T.; Calabrese, Edward J., Boca Raton : Lewis Publishers,; 1992.
x, 227 p. : ill. ; 25 cm. Association of American Railroads. Includes bibliographical references and index.

Language: English

Descriptors: Oil pollution of soils; Diesel fuels; Bioremediation

65 NAL Call. No.: RA565.A1E54 Contamination and restoration of groundwater aquifers. Piver, W.T.
Research Triangle Park, N.C. : National Institute of Environmental Health Sciences; 1993 Apr.
E.H.P. Environmental health perspectives v. 100: p. 237-247; 1993 Apr. Includes references.

Language: English

Descriptors: Groundwater pollution; Drinking water; Aquifers; Agricultural chemicals; Pollutants; Transport processes; Exposure; Bioremediation

66 NAL Call. No.: TA166.T72 Controlling environmental nitrogen through microbial metabolism. Cole, J.
Cambridge : Elsevier Science Publishing Co; 1993 Aug. Trends in biotechnology v. 11 (8): p. 368-372; 1993 Aug. In the special issue: Bioremediation: technological and commercial issues in the biological detoxification of polluted sites. Includes references.

Language: English

Descriptors: Pollution control; Pollutants; Nitrogen; Nitrogen fixing bacteria; Denitrifying microorganisms; Bioremediation

Abstract: The major sources of environmental nitrogen are the result of process intensification by human activities such as the chemical synthesis of nitrogenous fertilizers, internal-combustion engines, intensive farming and the use of xenobiotic chemicals in industrial processes. Recent advances in the biochemistry, genetics and ecology of nitrifying and denitrifying bacteria can now be exploited in the control of environmental pollution from these sources. However, frequently, biotreatment must be combined with physical and chemical processes to achieve satisfactory remediation.


67                                                 NAL Call. No.: RA1270.P35A1
                                                               NSURA1270.P35A1

Copper toxicity towards a pentachlorophenol-degrading flavobacterium sp. Wall, A.J.; Stratton, G.W.
New York : Springer-Verlag, 1966-; 1994 Apr. Bulletin of environmental contamination and toxicology v. 52 (4): p. 590-597; 1994 Apr. Includes references.

Language: English

Descriptors: Pentachlorophenol; Copper; Toxicity; Flavobacterium; Microbial degradation; Growth; Bioremediation

68 NAL Call. No.: TD420.A1P7 Cross-flow ultrafiltration used in algal high rate oxidation pond treatment of saline organic effluents with the recovery of products of value. Rose, P.D.; Maart, B.A.; Phillips, T.D.; Tucker, S.L.; Cowan, A.K.; Rowswell, R.A.
Oxford ; New York : Pergamon Press, c1981-; 1992. Water science and technology : a journal of the International Association on Water Pollution Research v. 25 (10): p. 319-327; 1992. In the series analytic: Mexico technology in wastewater management / edited by O.O. Hart and C.A. Buckley. Proceedings of the International Specialized Conference, March 2-5, 1992, Cape Town, South Africa. Includes references.

Language: English

Descriptors: South Africa; Cabt; Tannery waste; Salinity; Waste water treatment; Oxidation; Ponds; Dunaliella; Ultrafiltration; Algae; Biotechnology

69 NAL Call. No.: 381 J8224 Degradation kinetics of pentachlorophenol by Phanerochaete chrysosporium. Lin, J.E.; Wang, H.Y.; Hickey, R.F.
New York, N.Y. : John Wiley & Sons; 1990 May. Biotechnology and bioengineering v. 35 (11): p. 1125-1134; 1990 May. Includes references.

Language: English

Descriptors: Phanerochaete chrysosporium; Ligninolytic microorganisms; Yeast extracts; Enzymes; Pentachlorophenol; Microbial degradation; Kinetics; Models

Abstract: The extracellular enzymes and cell mass from the pregrown Phanerochaete chrysosporium cultures were used for the degradation of PCP. The use of both extracellular enzymes and cell mass resulted in extensive mineralization of PCP, while the action of only the crude extracellular enzymes led to the formation of a degradation intermediate (TCHD). A kinetic model, which describes the relationship among PCP degradation, initial PCP concentration, dosage of extracellular enzymes, and cell mass concentration, was developed. Based on this model, various effects of initial PCP concentration, dosage of extracellular enzymes, and cell mass concentration were evaluated experimentally. It was found that when initial PCP concentration is lower than 12 micromol/L, the model of a parallel-series first-order reaction is sufficient to describe the degradation process. PCP disappearance and mineralization were enhanced by increasing either the extracellular enzyme concentration or the cell mass concentration. As high as 70% of PCP mineralization could be obtained by using a higher dosage of extracellular enzymes and cell mass. Various parameters of the kinetic model were determined and the model was verified experimentally. Simulation using this model provided the criteria needed to choose rational dosages of extracellular enzymes and cell mass for the degradation of PCP. Data reported allow some insight into the function of the extracellular enzymes and cell mass of P. chrysosporium in degradation processes of toxic pollutants and assist in the design and evaluation of practical bioremediation methods.

70 NAL Call. No.: QR1.F44 Degradation of Aroclor 1221 in soil by a hybrid pseudomonad. Havel, J.; Reineke, W.
Amsterdam : Elsevier Science Publishers; 1993 Apr01. FEMS microbiology letters - Federation of European Microbiological Societies v. 108 (2): p. 211-218; 1993 Apr01. Includes references.

Language: English

Descriptors: Pseudomonas cepacia; Soil bacteria; Hybrids; Polychlorinated biphenyls; Metabolites; Microbial degradation; Bioremediation; Soil pollution

Abstract: The hybrid Pseudomonas cepacia strain JHR22 was tested for its ability to degrade Aroclor 1221 in soil. The influence of supplements-mineral salts and trace elements-on the degradation was investigated. Disappearance of Aroclor 1221 congeners, occurrence of metabolites, and release of chloride were measured under different conditions. After 45 days the hybrid organism, strain JHR22, was still present at high numbers in soil, independently of whether the soil had been sterilized prior to inoculation or not. There was only a minor difference in degradation efficiency between sterilized and untreated soil with about 70% release of chloride when 10(7) cells/g soil were inoculated. The whole hybrid pathway, originating from three different strains, was found to be stable under the conditions tested. Mineral salts did not significantly affect the degradation rate or survival of the hybrid strain.

71 NAL Call. No.: 448.3 AP5 Degradation of azo dyes by the lignin-degrading fungus Phanerochaete chrysosporium.
Spadaro, J.T.; Gold, M.H.; Renganathan, V. Washington, D.C. : American Society for Microbiology; 1992 Aug. Applied and environmental microbiology v. 58 (8): p. 2397-2401; 1992 Aug. Includes references.

Language: English

Descriptors: Phanerochaete chrysosporium; Biodegradation; Mineralization; Dyes

Abstract: Under nitrogen-limiting, secondary metabolic conditions, the white rot basidiomycete Phanerochaete chrysosporium extensively mineralized the specifically 14C-ring-labeled azo dyes 4-phenylazophenol, 4-phenylazo-2-methoxyphenol, Disperse Yellow 3 [2-(4'-acetamidophenylazo)-4-methylphenol], 4-phenylazoaniline, N,N-dimethyl-4-phenylazoaniline, Disperse Orange 3 [4-(4'-nitrophenylazo)-aniline], and Solvent Yellow 14 (1-phenylazo-2-naphthol). Twelve days after addition to cultures, the dyes had been mineralized 23.1 to 48.1%. Aromatic rings with substituents such as hydroxyl, amino, acetamido, or nitro functions were mineralized to a greater extent than unsubstituted rings. Most of the dyes were degraded extensively only under nitrogen-limiting, ligninolytic conditions. However, 4-phenylazo-[U-14C]phenol and 4-phenylazo-[U-14C]2-methoxyphenol were mineralized to a lesser extent under nitrogen-sufficient, nonligninolytic conditions as well. These results suggest that P. chrysosporium has potential applications for the cleanup of textile mill effluents and for the bioremediation of dye-contaminated soil.

72 NAL Call. No.: TP248.13.B55 Degradation of halogenated hydrocarbons. Wilson, J.T.
Stuttgart, W. Ger. : Gustav Fischer; 1988. Biotec (2): p. 75-77; 1988. Includes references.

Language: English

Descriptors: Groundwater pollution; Halogenated hydrocarbons; Microbial degradation; Aquifers; Biological treatment; Bioreactors

73 NAL Call. No.: QD415.A1J62 Degradation of munition wastes by Phanerochaete chrysosporium. Sublette, K.L.; Ganapathy, E.V.; Schwartz, S. Totowa, N.J. : Humana Press; 1992.
Applied biochemistry and biotechnology v. 34/35: p. 709-723; 1992. Paper presented at the "Thirteenth Symposium on Biotechnology for Fuels and Chemicals," May 6-10, 1991, Colorado Springs, Colorado. Includes references.

Language: English

Descriptors: Phanerochaete chrysosporium; Microbial degradation; Biological treatment; Waste water treatment; Waste water; Explosives; Rotating biological contactors

74 NAL Call. No.: SB599.C8 Degradation of pesticides by micro-organisms and the potential for genetic manipulation.
Mulbry, W.; Kearney, P.C.
Guildford : Butterworths; 1991 Oct.
Crop protection v. 10 (5): p. 334-346; 1991 Oct. Literature review. Includes references.

Language: English

Descriptors: Pentachlorophenol; Organophosphate insecticides; Triazine herbicides; 2,4-d; 2,4,5-t; Carbamate pesticides; Microbial degradation; Metabolic detoxification; Pesticide residues; Biochemical pathways; Enzyme activity; Genetic regulation; Microorganisms; Genes; Genetic engineering; Waste treatment; Literature reviews

75 NAL Call. No.: 448.3 Ap5 Degradation of trichloroethylene by Pseudomonas cepacia G4 and the constitutive mutant strain G4 5223 PR1 in aquifer microcosms. Krumme, M.L.; Timmis, K.N.; Dwyer, D.F. Washington : American Society for Microbiology; 1993 Aug. Applied and environmental microbiology v. 59 (8): p. 2746-2749; 1993 Aug. Includes references.

Language: English

Descriptors: Pseudomonas cepacia; Trichloroethylene; Microbial degradation; Oxygenases; Enzyme activity; Groundwater pollution; Aquifers; Groundwater; Bioremediation

Abstract: Pseudomonas cepacia G4 degrades trichloroethylene (TCE) via a degradation pathway for aromatic compounds which is induced by substrates such as phenol and tryptophan. P. cepacia G4 5223 PR1 (PR1) is a Tn5 insertion mutant which constitutively expresses the toluene ortho-monooxygenase responsible for TCE degradation. In groundwater microcosms, phenol-induced strain G4 and noninduced strain PR1 degraded TCE (20 and 50 micromolar) to nondetectable levels (<0.1 micromolar) within 24 h at densities of 100 cells per ml; at lower densities, degradation of TCE was not observed after 48 h. In aquifer sediment microcosms, TCE was reduced from 60 to <0.1 micromolar within 24 h at 5 X 10(8) PR1 organisms per g (wet weight) of sediment and from 60 to 26 micromolar over a period of 10 weeks at 5 X 10(7) PR1 organisms per g. Viable G4 and PR1 cells decreased from approximately 10(7) to 10(4) per g over the 10-week period.

76 NAL Call. No.: QH540.S8 Detoxification of phenol polluted soil by some Nocardia and Basidomycetes. Malarczyk, E.; Lewicka-Krol, Z.; Kochmanska-Rdest, J.; Apalovic, R.; Staszczak, M.; Leonowicz, A.
New York, N.Y. : Elsevier Science Publishing Company Inc; 1991. Studies in environmental science (42): p. 209-214; 1991. In the series analytic: Environmental biotechnology / edited by A. Blazej and V. Privarova. Proceedings of the International Symposium on Biotechnology, June 27-29, 1990, Bratislava, Czechoslovakia. Includes references.

Language: English

Descriptors: Nocardia; Pleurotus ostreatus; Inonotus; Coriolus versicolor; Microbial degradation; Phenol; Metabolic detoxification; Soil pollution; Polluted soils; Sawdust; Wood dust; Soil amendments; Phytotoxicity; Avena sativa; Festuca rubra

77 NAL Call. No.: 448.3 Ap5 Development of field application vectors for bioremediation of soils contaminated with polychlorinated biphenyls. LaJoie, C.A.; Zylstra, G.J.; DeFlaun, M.F.; Strom, P.F. Washington : American Society for Microbiology; 1993 Jun. Applied and environmental microbiology v. 59 (6): p. 1735-1741; 1993 Jun. Includes references.

Language: English

Descriptors: Pseudomonas; Gene transfer; Plasmid vectors; Genes; Polychlorinated biphenyls; Microbial degradation; Bioremediation; Polluted soils; Nonionic surfactants; Inoculum; Metabolism; Biphenyl; Recombinant DNA

Abstract: Field application vectors (FAVs), which are a combination of a selective substrate, a host, and a cloning vector, have been developed for the purpose of expressing foreign genes in nonsterile, competitive environments in which the gene products provide no advantage to the host. Such gene products are exemplified by the enzymes for the cometabolism of polychlorinated biphenyls (PCBs) through the biphenyl degradation pathway. Attempts to use highly competent PCB-cometabolizing strains in the environment in the absence of biphenyl have not been successful, while the addition of biphenyl is limited by its human toxicity and low water solubility. Broad-substrate-specificity PCB-degradative genes (bphABC) were cloned from a naturally occurring isolate, Pseudomonas sp. strain ENV307, into broad-host-range plasmid pRK293. The resulting PCB-degrading plasmids were transferred to the FAV host Pseudomonas paucimobilis 1IGP4, which utilizes the nontoxic, water-soluble, nonionic surfactant Igepal CO-720 as a selective growth substrate. Plasmid stability in the recombinant strains was determined in the absence of antibiotic selection. PCB-degrading activity was determined by resting cell assays. Treatment of contaminated soil (10, 100, or 1,000 ppm of Aroclor 1242) by surfactant amendment (1.0% [wt/wt]Igepal CO-720 in wet soil) and inoculation with recombinant isolates of strain 1IGP4 (approximately 4 X 10(6) cells per g of soil) resulted in degradation of many of the individual PCB congeners in the absence of biphenyl. Further improvements, including the use of non-antibiotic-resistance cloning vectors, addition of the bphD gene, and chromosomal integration of the PCB-degradative genes, may ultimately result in FAVs useful for both reactor-contained and in situ treatment of the partially dechlorinated PCBs often found in contaminated soils and sediments.

78 NAL Call. No.: TD420.A1E5 Ecological engineering.
Mitsch, W.J.
Washington, D.C. : American Chemical Society; 1993 Mar. Environmental science & technology v. 27 (3): p. 438-445; 1993 Mar. Includes references.

Language: English

Descriptors: Environmental degradation; Pollution; Ecosystems; Nature conservation; Biotechnology

79 NAL Call. No.: TA166.T72 Ecology and evolution of microbial populations for bioremediation. Liu, S.; Suflita, J.M.
Cambridge : Elsevier Science Publishing Co; 1993 Aug. Trends in biotechnology v. 11 (8): p. 344-352; 1993 Aug. In the special issue: Bioremediation: technological and commercial issues in the biological detoxification of polluted sites. Includes references.

Language: English

Descriptors: Contaminants; Microbial degradation; Bioremediation; Microorganisms; Genetic variation; Ecology; Evolution; Physiology

Abstract: Bioremediation exploits the genetic diversity and metabolic versatility of microorganisms for the transformation of contaminants into less-harmful end-products, which are then integrated into natural biogeochemical cycles. Understanding the ecology, physiology and evolution of degradative microorganisms is critical for the successful consideration and implementation of bioremediation. This article focuses on the common ecological and evolutionary constraints that influence bioremediation processes.

80 NAL Call. No.: 448.3 AP5 Effect of 2-hydroxybenzoate on the maintenance of naphthalene-degrading pseudomonads in seeded and unseeded soil. Ogunseitan, O.A.; Delgado, I.L.; Tsai, Y.L.; Olson, B.H. Washington, D.C. : American Society for Microbiology; 1991 Oct. Applied and environmental microbiology v. 57 (10): p. 2873-2879; 1991 Oct. Includes references.

Language: English

Descriptors: Pseudomonas; Soil flora; Microbial degradation; Naphthalene; Phenolic acids; Salicylates; Catabolism; Gene expression; Structural genes; Induction; Population dynamics

Abstract: The addition of specific nontoxic inducers of catabolic operons to contaminated sites is an approach that may enhance the efficiency of in situ biodegradation. We determined the genetic response of six pseudomonads to salicylate (also known as 2-hydroxybenzoate) added directly to 50 g of nonsterile soil samples. The strains, isolated from a polyaromatic hydrocarbon-contaminated soil, metabolized naphthalene as the sole source of available carbon, and their DNA sequences show significant homology to the nahAB genes of the degradative plasmid NAH7. Duplicate nonsterile soil cultures were incubated for up to 30 days. Experimental soil cultures were seeded with naphthalene-degrading strains (10(8) CFU g-1) originally isolated from the soil and amended with salicylate (16 or 160 microgram g-1). Soil samples were analyzed periodically for the population density of heterotrophic bacteria and naphthalene degraders and for the abundance of the naphthalene-degradative genotype in the bacterial community. At 160 microgram g-1, salicylate sustained the density of naphthalene degraders at the introduced density for 30 days in addition to producing a two- to sixfold increase in the occurrence in the bacterial community of DNA sequences homologous to the nah operon. No change in recoverable bacterial population densities was observed when soil samples were amended with 16 microgram of salicylate g-1, but this concentration of salicylate induced a significant increase in the level of nah-related genes in the population.

81 NAL Call. No.: QR1.E9 Effect of a non-ionic surfactant added to the soil surface on the biodegradation of aromatic hydrocarbons within the soil. Aronstein, B.N.; Alexander, M.
Berlin ; New York : Springer International, [1984?-; 1993 Jun. Applied microbiology and biotechnology v. 39 (3): p. 386-390; 1993 Jun. Includes references.

Language: English

Descriptors: Soil; Surfactants; Aromatic hydrocarbons; Biodegradation

Abstract: A study was conducted to determine whether a non-ionic surfactant (Novel II 1412-56) added to the surface of Lima silt loam would enhance the biodegradation of phenanthrene and biphenyl present within the soil. Water containing the surfactant at concentrations of 10 and 100 micrograms/ml was pumped through the soil. At 10 micrograms/ml, Novel II 1412-56 markedly enhanced the rate and extent of phenanthrene mineralization and the extent but not the initial rate of biphenyl mineralization. The stimulation was less if the water added to the soil surface contained 100 micrograms surfactant/ml. Addition of the surfactant at the two concentrations did not result inleaching of either phenanthrene or biphenyl, but products of the degradation were found in the soil leachate with or without the surfactant. We suggest that surfactants at low concentrations may be useful for in-situ bioremediation of sites contaminated with hydrophobic pollutants without causing movement of the parent compounds to ground-waters.

82 NAL Call. No.: 448.3 AP5 Effect of inoculant strain and organic matter content on kinetics of 2,4-dichlorophenoxyacetic acid degradation in soil. Greer, L.E.; Shelton, D.R.
Washington, D.C. : American Society for Microbiology; 1992 May. Applied and environmental microbiology v. 58 (5): p. 1459-1465; 1992 May. Includes references.

Language: English

Descriptors: 2,4-d; Microbial degradation; Soil bacteria; Strains; Kinetics; Substrates; Soil organic matter; Bioavailability; Soil pollution

Abstract: We monitored rates of degradation of soluble and sorbed 2,4-dichlorophenoxyacetic acid (2,4-D) in low-organic-matter soil at field capacity amended with 1, 10, or 100 microgram of 2,4-D per g of wet soil and inoculated with one of two bacterial strains (MI and 155) with similar maximum growth rates (micro(max)) but significantly different half-saturation growth constants (Ks). Concentrations of soluble 2,4-D were determined by analyzing samples of pore water pressed from soil, and concentrations of sorbed 2,4-D were determined by solvent extraction. Between 65 and 75% of the total 2,4-D was present in the soluble phase at equilibrium, resulting in soil solution concentrations of ca. 8, 60, and 600 microgram of 2,4-D per ml, respectively. Soluble 2,4-D was metabolized preferentially; this was followed by degradation of both sorbed (after desorption) and soluble 2,4-D. Rates of degradation were comparable for the two strains at soil concentrations of 10 and 100 microgram of 2,4-D per g; however, at 1 microgram/g of soil, 2,4-D was metabolized more rapidly by the strain with the lower Ks value (strain MI). We also monitored rates of biodegradation of soluble and sorbed 2,4-D in high-organic-matter soil at field capacity amended with 100 microgram of 2,4-D per g of wet soil and inoculated with the low-Ks strain (strain MI). Ten percent of total 2,4-D was present in the soluble phase, resulting in a soil solution concentration of ca. 30 microgram of 2,4-D per ml. Rates of degradation in the high-organic-matter soil were lower than in the low-organic-matter soil, presumably as a result of lower rates of desorption and microbial growth.

83 NAL Call. No.: 448.3 AP5 Effect of sodium chloride on transport of bacteria in a saturated aquifer material.
Gannon, J.; Tan, Y.; Baveye, P.; Alexander, M. Washington, D.C. : American Society for Microbiology; 1991 Sep. Applied and environmental microbiology v. 57 (9): p. 2497-2501; 1991 Sep. Includes references.

Language: English

Descriptors: Aquifers; Sand; Transport processes; Pseudomonas; Sodium chloride; Flow; Velocity; Saturated conditions

Abstract: Determinations were made of the influence of NaCl concentration, cell density, and flow velocity on the transport of Pseudomonas sp. strain KL2 through columns of aquifer sand under saturated conditions. A pulse-type boundary condition was used. The experiments were conducted by using 0.3-m-long Plexiglas columns with an internal diameter of 0.05 m. When a 1-h pulse of a 0.01 M NaCl solution containing 10(8) cells per ml was added at a flow rate of 10(-4) m s-1, the bacterial density in the effluent never exceeded 2.2% of the density of cells added, and only 1.5% of the bacteria passed through the aquifer material. In contrast, when the bacteria were applied in distilled water, the relative cell density in the effluent approached 100%, and 60% of the bacteria were transported through the aquifer solids. Under these conditions, the breakthrough of Pseudomonas sp. strain KL2 was slower than chloride. When the flow rate was 2.0 X 10(-4) M S-1, the cell density in the effluent reached 7.3% of that added in 0.01 M NaCl solution, but only 3.9% of the bacteria were transported through the aquifer particles. On the other hand, the density in the effluent approached 100% of that added in deionized water, and 77% of the added bacteria were recovered. When the density of added cells was 10(9) cells per ml at a flow rate of 10(-4) M S-1, the densities in the effluent reached 70 and 100% of those added in salt solution and deionized water, respectively, and 44 and 57% of the bacteria were transported through the aquifer solids. Replacement of the NaCl solution with deionized water caused some of the retained cells to be carried through the column. We suggest that the movement of bacteria added to sandy aquifers for bioremediation of contaminated sites may be promoted by modifying the chemical composition of the carrying solution.

84 NAL Call. No.: 448.3 Ap5 Effect of treated-sewage contamination upon bacterial energy charge, adenine nucleotides, and DNA content in a sandy aquifer on Cape Cod. Metge, D.W.; Brooks, M.H.; Smith, R.L.; Harvey, R.W. Washington : American Society for Microbiology; 1993 Jul. Applied and environmental microbiology v. 59 (7): p. 2304-2310; 1993 Jul. Includes references.

Language: English

Descriptors: Massachusetts; Cabt; Aquifers; Bacteria; Groundwater pollution; Sewage effluent; Sewage effluent disposal; Application to land; Dna; Adenosine phosphates; Energy content

Abstract: Changes in adenylate energy charge (EC(A)) and in total adenine nucleotides (A(T)) and DNA content (both normalized to the abundance of free-living, groundwater bacteria) in response to carbon loading were determined for a laboratory-grown culture and for a contaminated aquifer. The latter study involved a 3-km-long transect through a contaminant plume resulting from continued on-land discharge of secondary sewage to a shallow, sandy aquifer on Cape Cod, Mass. With the exception of the most contaminated groundwater immediately downgradient from the contaminant source, DNA and adenylate levels correlated strongly with bacterial abundance and decreased exponentially with increasing distance downgradient. EC(A)s (0.53 to 0.60) and the ratios of ATP to DNA (0.001 to 0.003) were consistently low, suggesting that the unattached bacteria in this groundwater study are metabolically stressed, despite any eutrophication that might have occurred. Elevated EC(A)s (up to 0.74) were observed in glucose-amended groundwater, confirming that the metabolic state of this microbial community could be altered. In general, per-bacterium DNA and ATP contents were approximately twofold higher in the plume than in surrounding groundwater, although EC(A) and per-bacterium levels of A(T) differed little in the plume and the surrounding uncontaminated groundwater. However, per-bacterium levels of DNA and A(T) varied six- and threefold, respectively, during a 6-h period of decreasing growth rate for an unidentified pseudomonad isolated from contaminated groundwater and grown in batch culture. These data suggest that the DNA content of groundwater bacteria may be more sensitive than their to the degree of carbon loading, which may have significant ramifications in the use of nucleic acids and adenine nucleotides for estimating the metabolic status of bacterial communities within more highly contaminated aquifers.

85 NAL Call. No.: 448.3 Ap5 Effects of medium and trace metals on kinetics of carbon tetrachloride transformation by Pseudomonas sp. strain KC. Tatara, G.M.; Dybas, M.J.; Criddle, C.S. Washington : American Society for Microbiology; 1993 Jul. Applied and environmental microbiology v. 59 (7): p. 2126-2121; 1993 Jul. Includes references.

Language: English

Descriptors: Pseudomonas; Carbon tetrachloride; Microbial degradation; Metal ions; Copper; Ferric ions; Ph; Groundwater pollution; Aquifers; Groundwater; Bioremediation; Nutrient availability; Nitrate; Acetic acid

Abstract: Under denitrifying conditions, Pseudomonas sp. strain KC transforms carbon tetrachloride (CT) to carbon dioxide via a complex but as yet undetermined mechanism. Transformation rates were first order with respect to CT concentration over the CT concentration range examined (O to 100 microgram/liter) and proportional to protein concentration, giving pseudo-second-order kinetics overall. Addition of ferric iron (1 to 20 micromolar) to an actively transforming culture inhibited CT transformation, and the degree of inhibition increased with increasing iron concentration. By removing iron from the trace metals solution or by removing iron-containing precipitate from the growth medium, higher second-order rate coefficients were obtained. Copper also plays a role in CT transformation. Copper was toxic at neutral pH. By adjusting the medium pH to 8.2, soluble iron and copper levels decreased as a precipitate formed, and CT transformation rates increased. However, cultures grown at high pH without any added trace copper (1 micromolar) exhibited slower growth rates and greatly reduced rates of CT transformation, indicating that copper is required for CT transformation. The use of pH adjustment to decrease iron solubility, to avoid copper toxicity, and to provide a selective advantage for strain KC was evaluated by using soil slurries and groundwater containing high levels of iron. In samples adjusted to pH 8.2 and inoculated with strain KC, CT disappeared rapidly in the absence or presence of acetate or nitrate supplements. CT did not disappear in pH-adjusted controls that were not inoculated with strain KC.

86 NAL Call. No.: 381 J8224 Effects of nonionic surfactants on the solubilization and mineralization of phenanthrene in soil-water systems.
Laha, S.; Luthy, R.G.
New York, N.Y. : John Wiley & Sons; 1992 Dec20. Biotechnology and bioengineering v. 40 (11): p. 1367-1380; 1992 Dec20. Includes references.

Language: English

Descriptors: Phenanthrene; Solubilization; Nonionic surfactants; Microbial degradation; Mineralization; Silt loam soils; Soil flora

Abstract: The solubilization and mineralization of 14C-phenanthrene in soil-water systems was examined with several commercially available surface-active agents, viz., an alkyl ethoxylate C12E4; two alkylphenol ethoxylate surfactants: C8PE95 and C9PE10.5; two sorbitan ethoxylate surfactants: the sorbitan monolaurate (Tween 20) and the sorbitan monooleate (Tween 80); two pairs of nonionic ethoxylate surfactant mixtures: C12E4/C12E23 at a 1:1 ratio, and C12-15E3/C12-15E9 at a 1:3 ratio; and two surfactants possessing relatively high critical micelle concentration (CMC) values and low aggregation numbers: CHAPS and octylglucoside. Surface tension experiments were performed to evaluate surfactant sorption onto soil and the surfactant doses required to attain the CMC in the soil-water systems. Surfactant solubilization of 14C-phenanthrene commenced with the onset of micellization. The addition of surface-active agents was observed not to be beneficial to the microbial mineralization of phenanthrene in the soil-water systems and, for supra-CMC surfactant doses, phenanthrene mineralization was completely inhibited for all the surfactants tested. A comparison of solubilization, surface tension, and mineralization data confirms that the inhibitory effect on microbial degradation of phenanthrene is related to the CMC of the surfactant in the presence of soil. Additional tests demonstrated the recovery of mineralization upon dilution of the surfactant concentration to sub-CMC levels, and a relatively high exit rate for phenanthrene from micelles. These tests suggest that the inhibitory effect is probably related to a reversible physiological surfactant micelle-bacteria interaction, possibly through partial complexing or release of membrane material without disrupting membrane lameilar structure. This study indicates that nonionic surfactant solubilization of sorbed hydrophobic organic compounds from soil may not be beneficial for the concomitant enhancement of soil bioremediation. Add

87 NAL Call. No.: 448.3 AP5 Enhanced biodegradation of phenanthrene in oil tar-contaminated soils supplemented with Phanerochaete chrysosporium. Brodkorb, T.B.; Legge, R.L.
Washington, D.C. : American Society for Microbiology; 1992 Sep. Applied and environmental microbiology v. 58 (9): p. 3117-3121; 1992 Sep. Includes references.

Language: English

Descriptors: Soil pollution; Pollutants; Tars; Microbial degradation; Phanerochaete chrysosporium; Phenanthrene; Mineralization

Abstract: In recent years, the white rot fungus Phanerocharte chrysosporium has shown promise as an organism suitable for the breakdown of a broad spectrum of environmental pollutants, including polynuclear aromatic hydrocarbons (PAHs). The focus of this study was to determine whether P. chrysosporium could effectively operate in an actual field sample of oil tar-contaminated soil. The soil was loaded with [14C]phenanthrene to serve as a model compound representative of the PAHs. Soil with the native flora present under static, aerobic conditions with buffering (pH 5.0 to 5.5) displayed full mineralization on the order of 20% in 21 days. The addition of P. chrysosporium was synergistic, with full mineralization on the order of 38% in 21 days. In addition to full mineralization, there was an increase in the proportion of radiolabelled polar extractives, both soluble and bound, in the presence of P. chrysosporium. From this study, it is apparent that the native soil microflora can be prompted into full mineralization of PAHs in some contaminated soils and that this mineralization can be enhanced when supplemented with the white rot fungus P. chrysosporium. With further refinement, this system may prove an effective bioremediation technology for soils contaminated with PAHs.

88 NAL Call. No.: 448.3 AP5 Enhanced mineralization of polychlorinated biphenyls in soil inoculated with chlorobenzoate-degrading bacteria.
Hickey, W.J.; Searles, D.B.; Focht, D.D. Washington, D.C. : American Society for Microbiology; 1993 Apr. Applied and environmental microbiology v. 59 (4): p. 1194-1200; 1993 Apr. Includes references.

Language: English

Descriptors: Soil bacteria; Pseudomonas aeruginosa; Pseudomonas putida; Polychlorinated biphenyls; Microbial degradation; Mineralization; Soil inoculation; Organochlorine compounds; Bioremediation

Abstract: An Altamont soil containing no measurable population of chlorobenzoate utilizers was examined for the potential to enhance polychlorinated biphenyl (PCB) mineralization by inoculation with chlorobenzoate utilizers, a biphenyl utilizer, combinations of the two physiological types, and chlorobiphenyl-mineralizing transconjugants. Biphenyl was added to all soils, and biodegradation of 14C-Aroclor 1242 was assessed by disappearance of that substance and by production of 14CO2. Mineralization of PCBs was consistently greatest (up to 25.5%) in soils inoculated with chlorobenzoate degraders alone. Mineralization was significantly lower in soils receiving all other treatments: PCB cometabolizer (10.7%); chlorobiphenyl mineralizers (8.7 and 14.9%); and mixed inocula of PCB cometabolizers and chlorobenzoate utilizers (11.4 and 18.0%). However, all inoculated soils had higher mineralization than did the uninoculated control (3.1%). PCB disappearance followed trends similar to that observed with the mineralization data, with the greatest degradation occurring in soils inoculated with the chlorobenzoate-degrading strains Pseudomonas aeruginosa JB2 and Pseudomonas putida P111 alone. While the mechanism by which the introduction of chlorobenzoate degraders alone enhanced biodegradation of PCBs could not be elucidated, the possibility that chlorobenzoate inoculants acquired the ability to metabolize biphenyl and possibly PCBs was explored. When strain JB2, which does not utilize biphenyl, was inoculated into soil containing biphenyl and Aroclor 1242, the frequency of isolates able to utilize biphenyl and 2,5-dichlorobenzoate increased progressively with time from 3.3 to 44.4% between 15 and 48 days, respectively. Since this soil contained no measurable level of chlorobenzoate utilizers yet did contain a population of biphenyl utilizers, the possibility of genetic transfer between the latter group and strain JB2 cannot be excluded.

89 NAL Call. No.: TP1.J686 Enhanced removal of selected hydrocarbons from soil by Pseudomonas aeruginosa UG2 biosurfactants and some chemical surfactants. Scheilbenbogen, K.; Zytner, R.G.; Lee, H.; Trevors, J.T. Essex : Elsevier Applied Science Publishers; 1994 Jan. Journal of chemical technology and biotechnology v. 59 (1): p. 53-59; 1994 Jan. Includes references.

Language: English

Descriptors: Pseudomonas aeruginosa; Surfactants; Glycolipids; Bioremediation; Soil pollution; Polluted soils; Hydrocarbons; Sandy loam soils

90 NAL Call. No.: TD172.E55 v.41 Environmental biotechnology for waste treatment. Sayler, Gary S.,_1949-; Fox, Robert; Blackburn, James W., Symposium on Environmental Biotechnology: Moving from the Flask to the Field 1990 : Knoxville, Tenn.
New York : Plenum Press,; 1991.
ix, 288 p. : ill. ; 26 cm. (Environmental science research ; v. 41). "Proceedings of the Symposium on Environmental Biotechnology: Moving from the Flask to the Field, held October 17-19, 1990, in Knoxville, Tennessee"--T.p. verso. Includes bibliographical references and index.

Language: English

Descriptors: Environmental biotechnology

91 NAL Call. No.: QD415.A1J62 Environmental influences on diethyl phthalate biodegradation kinetics. Reardon, K.F.; Zhang, G.
Totowa, N.J. : Humana Press; 1992.
Applied biochemistry and biotechnology v. 34/35: p. 753-765; 1992. Paper presented at the "Thirteenth Symposium on Biotechnology for Fuels and Chemicals," May 6-10, 1991, Colorado Springs, Colorado. Includes references.

Language: English

Descriptors: Soil flora; Soil bacteria; Microbial degradation; Phthalates; Cell suspensions; Dissolved oxygen; Bioremediation; Temperature

92 NAL Call. No.: QD1.A45 no.509 Environmental remediation removing organic and metal ion pollutants. Vandegrift, G. F._1945-; Reed, Donald Timothy,_1956-; Tasker, I. R. American Chemical Society, Division of Industrial and Engineering Chemistry, American Chemical Society, Meeting_1991 :_Atlanta, Ga.) Washington, DC : American Chemical Society,; 1992. xii, 275 p. : ill. ; 24 cm. (ACS Symposium series, 509). Developed from a symposium sponsored by the Division of Industrial and Engineering Chemistry, Inc., at the 201st National Meeting of the American Chemical Society, Atlanta, Georgia, April 14-19, 1991. Includes bibliographical references and indexes.

Language: English

Descriptors: Water, Underground; Soil pollution; Separation (Technology); Bioremediation

93 NAL Call. No.: QR53.B56 An enzyme biotechnology for the total utilization of leather wastes. Dalev, P.G.; Simeonova, L.S.
Middlesex : Science and Technology Letters; 1992 Jun. Biotechnology letters v. 14 (6): p. 531-534; 1992 Jun. Includes references.

Language: English

Descriptors: Leather waste; Waste utilization; Carrion; Animal proteins; Animal fat; Fractionation; Proteinases; Digestion; Biological production

Abstract: The isolation of protein and fat fractions from a waste of the leather industry is discussed. This represents the main waste of leather production and gives rise to problems of ecological and economical nature. A middle capacity factory deposits about 30 tons of the so called carrion, a source for the production of about 3 t useful products - protein and fat.

94 NAL Call. No.: QH431.G452 Field performance and heavy metal concentrations of transgenic flue-cured tobacco expressing a mammalian metallothionein-beta-glucuronidase gene fusion. Brandle, J.E.; Labbe, H.; Hattori, J.; Miki, B.L. Ottawa : National Research Council of Canada; 1993 Apr. Genome v. 36 (2): p. 255-260; 1993 Apr. Includes references.

Language: English

Descriptors: Nicotiana tabacum; Transgenic plants; Genetic transformation; Recombinant DNA; Metallothionein; Structural genes; Beta-glucuronidase; Reporter genes; Gene expression; Cadmium; Uptake; Leaves; Roots

Abstract: Cadmium (Cd) is a nonessential heavy metal that can cause acute and chronic illness in humans. Some plant species such as tobacco (Nicotiana tabacum L.) tend to accumulate high levels of Cd in leaf tissue, the consumed portion of the plant. Tissue-specific expression of mammalian metallothionein has been suggested as a means of partitioning Cd in nonconsumed portions of transgenic plants. The purpose of the experiment reported here was to evaluate Cd concentration and agronomic performance of four field-grown transgenic tobacco lines harbouring a metallothionein-beta-glucuronidase (MG) gene fusion driven by the constitutive 35S promoter of cauliflower mosaic virus. The trial was grown in a region of Canada known to have high background levels of Cd. The agronomic evaluation showed that some of the transgenic lines were equal to, while others performed more poorly than, the untransformed control for yield, days to flower, and leaf number. Gene expression measured by beta-glucuronidase activity showed that all of the transgenic lines expressed the MG gene in the upper portion of the plant. One line did not express the MG gene in the roots. Cd levels in the leaf tissue of transformed lines were not significantly different from the untransformed control.

95 NAL Call. No.: QD415.A1J62 Fungal degradation of organophosphorous insecticides. Bumpus, J.A.; Kakar, S.N.; Coleman, R.D. Totowa, N.J. : Humana Press; 1993.
Applied biochemistry and biotechnology v. 39/40: p. 715-726; 1993. Paper presented at the Fourteenth Symposium on Biotechnology for Fuels and Chemicals held May 11-15, 1992, Gathinburg, Tennessee. Includes references.

Language: English

Descriptors: Phanerochaete chrysosporium; Microbial degradation; Chlorpyrifos; Fonofos; Terbufos

96 NAL Call. No.: QH540.S8 The future of the lignocellulosic wastes bioconversion. Spilda, I.; Blazej, A.; Kosik, M.
New York, N.Y. : Elsevier Science Publishing Company Inc; 1991. Studies in environmental science (42): p. 201-208; 1991. In the series analytic: Environmental biotechnology / edited by A. Blazej and V. Privarova. Proceedings of the International Symposium on Biotechnology, June 27-29, 1990, Bratislava, Czechoslovakia. Includes references.

Language: English

Descriptors: Lignocellulosic wastes; Lignocellulose; Cellulose digestion; Microbial degradation; Cellulolytic microorganisms; Xylose; Glucose; Fermentation; Fermentation products

97 NAL Call. No.: 443.8 H42 A general model for the genetic control of copper tolerance in Silene vulgaris: evidence from crosses between plants from different tolerant populations.
Schat, H.; Kuiper, E.; Bookum, W.M. ten; Vooijs, R. Oxford : Blackwell Scientific Publications; 1993 Feb. Heredity v. 70 (pt.2): p. 142-147; 1993 Feb. Includes references.

Language: English

Descriptors: Silene vulgaris; Major genes; Copper; Metal tolerance; Segregation; Crossing; Populations; Gene interaction; Modifiers; Heterogeneity; Roots; Growth rate; Crosses

Abstract: Copper tolerance in Silene vulgaris seems to be controlled by two major genes. One segregates only in crosses to non-tolerants but never in crosses between tolerants originating from different isolated populations. The second segregates only in crosses to plants from the most tolerant population. The level of tolerance in tolerant plants seems to be controlled by two additional genes, which are hypostatic to the first major gene. They segregate in crosses to non-tolerants but not in crosses between equally homozygous tolerant plants from different populations. It is argued that all the genes are involved in the control of an exclusion mechanism operating at the plasmalemma.

98 NAL Call. No.: SB123.57.I55 1992 Genetic adaptation of bacteria towards chlorinated hydrocarbon degradation. Ploeg, J. van der; Pries, F.; Wijngaard, A. van den; Kennes, C.; Janssen, D.B. Braunschweig, Germany : Biologische Bundesanstalt fur Land- und Forstwirtschaft; 1992.
Proceedings of the 2nd International Symposium on the Biosafety Results of Field Tests of Genetically Modified Plants and Microorganisms : May 11-14, 1992, Goslar, Germany : edited by R. Casper and J. Landsmann. p. 163-169; 1992. Includes references.

Language: English

Descriptors: Bacteria; Genetic engineering; Microbial degradation; Chlorinated hydrocarbons; Decontamination

99 NAL Call. No.: QK725.I43 Genetic improvement of tree species for remediation of hazardous wastes. Stomp, A.M.; Han, K.H.; Wilbert, S.; Gordon, M.P. Columbia, MD : Tissue Culture Association, c1991-; 1993 Oct. In vitro cellular & developmental biology. Plant : journal of the Tissue Culture Association v. 29P (4): p. 227-232; 1993 Oct. Paper presented at the "Session-in-Depth Bioremediation through Biotechnological Means" at the 1993 Congress on Cell and Tissue Culture, June 5-9, 1993, San Diego, California. Includes references.

Language: English

Descriptors: Trees; Forest trees; Tree breeding; Bioremediation; Pollutants; Uptake; Metabolic detoxification; Metal tolerance; Genetic engineering; Genetic transformation; Agrobacterium rhizogenes; Soil pollution; Polluted soils

100 NAL Call. No.: TD426.G754 1992 Groundwater remediation.
Charbeneau, R. J.; Bedient, Philip B.,_1948; Loehr, Raymond C. Lancaster [Pa.] : Technomic Pub. Co.,; 1992. xi, 188 p. : ill. ; 24 cm. (Water quality management library ; v. 8). Includes bibliographical references and index.

Language: English

Descriptors: Water, Underground; Soil pollution; Bioremediation

101 NAL Call. No.: S592.7.A1S6 Growth and biodegradation by white-rot fungi inoculated into soil. Morgan, P.; Lee, S.A.; Lewis, S.T.; Sheppard, A.N.; Watkinson, R.J. Exeter : Pergamon Press; 1993 Feb.
Soil biology and biochemistry v. 25 (2): p. 279-287; 1993 Feb. Includes references.

Language: English

Descriptors: Phanerochaete chrysosporium; Chrysosporium; Coriolus versicolor; Decay fungi; 3,4-dichloroaniline; Benzopyrene; Mineralization; Microbial degradation; Bioremediation; Polluted soils; Substrates; Carbon; Nutrient sources; Soil amendments; Soil pollution

Abstract: The colonization of sandy loam soil following inoculation with spore suspensions of the white-rot fungi Phanerochaete chrysosporium ATCC 24725 and Chrysosporium lignorum CL1 was confirmed by an epifluorescence microscopy-image analysis method. These fungi and Trametes versicolor PV1 mineralized 3,4-dichloroaniline and benzo(a)pyrene in soil at concentrations up to 250 microgram g-1. Successful inoculation and biodegradation required supplementary carbon sources. Addition of inorganic nutrients had no stimulatory effect. Glucose, hay, wood chips, pine bark, loam and peat all promoted growth and degradation but chopped wheat straw was the best substrate. Increasing the content of straw in the soil led to increased biomass and mineralization. The optimum ratio of straw: soil for mineralization was 1:4. Both strains sporulated within 7 days of inoculation before a further increase in hyphal growth but this had no effect on the mineralization rate. These results indicate that use of white-rot fungi in biotechnological soil treatment may be feasible.

102 NAL Call. No.: QH540.J6 Growth and trace element concentrations of five plant species grown in a highly saline soil.
Retana, J.; Parker, D.R.; Amrhein, C.; Page, A.L. Madison : American Society Of Agronomy,; 1993 Oct. Journal of environmental quality v. 22 (4): p. 805-811; 1993 Oct. Includes references.

Language: English

Descriptors: California; Cabt; Grasses; Oryzopsis hymenoides; Astragalus racemosus; Salt tolerance; Boron; Metal tolerance; Genotypes; Heavy metals; Uptake; Electrical conductivity; Soil depth; Shoots; Yields; Bioremediation

Abstract: Kesterson Reservoir and other impoundments in the San Joaquin Valley, California, have received large volumes of saline irrigation drainage water that is enriched with trace elements, including As, B, Mo, Se, U, and V. When these ponds are allowed to dry and revert to terrestrial ecosystems, careful soil water and vegetation management may be needed to prevent toxicological hazards to wildlife and/or livestock. We conducted a 248-d column study in the greenhouse using a soil from Kesterson to assess the growth of salt- and B-tolerant genotypes, and to determine the uptake of As, B, Mo, Se, U, and V by these genotypes. Electrical conductivity decreased with soil depth, from 14 to 5 dS m-1, with B, Mo, Se, and U concentrations paralleling the soil salinity, whereas As and V were higher in the subsoil. Three grasses, alkali sacaton [Sporobolus airoides (Torr.) Torr.], tall wheatgrass [Elytrigia pontica (Podp.) Holub], Indian ricegrass [Oryzopsis hymenoides (Roem & Schult.)], and two Se-accumulators, Astragalus bisulcatus (Hook.) and A. racemosus Pursh., were successfully established after a preplanting leaching treatment to reduce salts in the seed zone. Three cuttings of alkali sacaton and tall wheatgrass resulted in total shoot yields of 11.1 and 7.6 g per column, respectively, but only 0.8 for a single cutting to the less salt- and B-tolerant Indian ricegrass. The slower-growing A. bisulcatus and A. racemosus yielded 3.8 and 4.4 g per column, respectively. Shoot concentrations of As, U, and V were low (< 3 mg kg-1) in all genotypes, and do not seem to pose food-chain transfer hazards at this site. Molybdenum and Se shoot concentrations of all genotypes exceeded the upper safe limits for consumption by ruminants, and shoot B concentrations were also high (> 60 mg kg-1). Despite high soil solution SO4 concentrations, both Astragalus species accumulated Se to high concentrations in the shoots (ca. 650 mg kg-1), and shoot harvest removed the equivalent of 2 to 3.5 kg Se ha-1. Growth of these Se-accumulating species shows promise as a means of direct removal of Se from Se-contaminated sites and could become a component of effective remediation strategies.

103 NAL Call. No.: TD426.J68 Hydrogen peroxide use to increase oxidant capacity for in situ bioremediation of contaminated soils and aquifers: a review. Pardieck, D.L.; Bouwer, E.J.; Stone, A.T. Amsterdam : Elsevier; 1992 Mar.
Journal of contaminant hydrology v. 9 (3): p. 221-242; 1992 Mar. Includes references.

Language: English

Descriptors: Soil pollution; Organic compounds; Aquifers; Pollutants; Biodegradation; Biological oxygen demand; Aerobiosis; Metabolism; Oxidation; Hydrogen peroxide; Groundwater pollution; Enzyme activity; Peroxidases; Reviews

104 NAL Call. No.: 448.3 Ap5 Hydroxylation and biodegradation of 6-methylquinoline by pseudomonads in aqueous and nonaqueous immobilized-cell bioreactors. Rothenburger, S.; Atlas, R.M.
Washington : American Society for Microbiology; 1993 Jul. Applied and environmental microbiology v. 59 (7): p. 2139-2144; 1993 Jul. Includes references.

Language: English

Descriptors: Pseudomonas putida; Quinoline; Derivatives; Quinolines; Microbial degradation; Chemical reactions; Bioreactors; Immobilization; Bioremediation

Abstract: Selective culturing of pseudomonads that could degrade quinoline led to enrichment cultures and pure cultures with expanded substrate utilization and transformation capabilities for substituted quinolines in immobilized and batch cultures. Immobilized cells of the pseudomonad cultures rapidly transformed quinolines to hydroxyquinolines in bioreactors and were able to tolerate higher substrate concentrations compared with batch cultures. After prolonged incubation on a mixture of quinoline and 6-methylquinoline, a quinoline-degrading culture of Pseudomonas putida developed the ability to biodegrade 6-methylquinoline, which initially was resistant to microbial attack, as a sole source of carbon and energy. 6-Methylquinoline was also degraded in a nonaqueous solution by this strain of P. putida when a solution of 6-methylquinoline in decane was flowed through an immobilized-cell fixed-bed bioreactor.

105 NAL Call. No.: TA166.T72 The impact of biochemistry, bioavailability and bioactivity on the selection of bioremediation techniques.
Blackburn, J.W.; Hafker, W.R.
Cambridge : Elsevier Science Publishing Co; 1993 Aug. Trends in biotechnology v. 11 (8): p. 328-333; 1993 Aug. In the special issue: Bioremediation: technological and commercial issues in the biological detoxification of polluted sites. Includes references.

Language: English

Descriptors: Soil pollution; Soil treatment; Pollution control; Bioremediation; Techniques; Biochemistry; Biological activity in soil; Bioavailability

Abstract: A wide range of bioremediation strategies is being developed to treat contaminated soils. Selecting the most appropriate strategy to treat a specific site can be guided by considering three basic principles: the amenability of the pollutant to biological transformation to less toxic products (biochemistry); the accessibility of the contaminant to microorganisms (bioavailability); and the opportunity for optimization of biological activity (bioactivity).

106 NAL Call. No.: 448.3 Ap5 In situ growth and activity and modes of penetration of Escherichia coli in unconsolidated porous materials.
Sharma, P.K.; McInerney, M.J.; Knapp, R.M. Washington : American Society for Microbiology; 1993 Nov. Applied and environmental microbiology v. 59 (11): p. 3686-3694; 1993 Nov. Includes references.

Language: English

Descriptors: Escherichia coli; Growth; Movement; Sand; Sandy soils; Mathematical models; Aquifers; Bioremediation; Pores; Pore size; Motility

Abstract: Statistically reliable data on the in situ rates of growth, substrate consumption, and product formation are required to test the validity of the mathematical models developed for microbially enhanced oil recovery and in situ bioremediation processes. A simple, replicable porous-core system that could be aseptically divided into sections at various times was developed to follow the kinetics of microbial growth and metabolism in situ. This core system was used to study the kinetics of growth and the mode of penetration of strains of Escherichia coli through anaerobic, nutrient-saturated, fine Ottawa sand (permeability of 7.0 micrometers(2) and porosity of 37%) under static conditions. The in situ rate of growth of a wild-type, motile, chemotactic strain, RW262, was two times slower inside cores than it was in liquid cultures. The mode of metabolism of galactose by strain RW262 was not altered inside cores, as acetate was the only product detected either inside the cores or in liquid cultures. Without applied advective force, strain RW262 grew exponentially and moved through cores at a rate of about 0.1 m/day. The cell population moved through cores in a band-like fashion, as the front of the moving cells consisted of high cell concentrations (greater than 10(5) cells per ml). Until the breakthrough of the cells occurred, galactose consumption and acetate production were observed only in the proximal sections of the core, showing that the cell propagation preceded the complete depletion of the substrate or the accumulation of large amounts of products. A motile, nonchemotactic strain of E. coli (RP5232) penetrated cores faster than did its chemotactic parental strain (RP437), which can be explained by differences in their mode of growth inside the cores. Unlike the wild-type, chemotactic strain RP437, which grew and moved through cores in a band-like fashion, cells of the nonchemotactic strain moved through cores in a diffuse manner, as the front of the moving cells consisted of low cell concentrations (10(3) cells per ml). The appearance of nonchemotactic cells in a section of the core was not necessarily followed by an increase in cell concentration in that section with time. For the nonmotile strain RP2912, a high cell density (10(7) cells per ml) in a section of the core was observed before cells were detected in the next section. This suggested that the transport of nonmotile cells through porous material requires a high cell density and may occur by a physical displacement process in which some of the progeny cells are forced into the less populated regions of the core.

107 NAL Call. No.: 292.8 W295 In situ measurement of microbial activity and controls on microbial CO2 production in the unsaturated zone.
Wood, B.D.; Keller, C.K.; Johnstone, D.L. Washington, D.C. : American Geophysical Union; 1993 Mar. Water resources research v. 29 (3): p. 647-659; 1993 Mar. Includes references.

Language: English

Descriptors: Washington; Saskatchewan; Carbon dioxide; Respiration; Microbial activities; Biological activity in soil; Measurement; Subsurface layers; Soil depth; Soil temperature; Correlation; Seasonal fluctuations; Bioremediation

Abstract: Carbon dioxide concentrations were measured at various depths and times in the unsaturated zones of two hydraulically and geochemically contrasting field sites, one in southeastern Washington state, and the other in south central Saskatchewan. In situ CO2 production rates were calculated from a mass balance that accounted for diffusive fluxes and partitioning of CO2 into an adverting aqueous phase. Production rates were compared with (1) microbial abundance and (2) subsurface temperature to determine whether subsurface CO2 production rates could be expressed as a simple function of these two variables. At the Washington site, subsurface production was successfully expressed as a function of microbial abundance and temperature for a large portion of the year, but not near the end of the growing season. Although subsurface microbes and organic carbon were more abundant at the Saskatchewan site, subsurface CO2 production rates were generally several orders of magnitude lower than at the Washington site, and no correlation could be established between microbial numbers, temperature, and production rate. The cases where production rates could not be expressed as a function of microbial numbers and temperature suggested conditions in which some other factor, such as nutrient limitations, was controlling.

108 NAL Call. No.: QR1.F44 Increased expression of the plamsid-determined 2,3-dihydroxybiphenyl dioxygenase gene in strains of Escherichia coli, Pseudomonas putida and Pseudomonas aeruginosa.
Andreyeva, A.L.; Slepenkyn, A.V.; Starovoytov, I.I. Amsterdam : Elsevier Science Publishers; 1993 Jan15. FEMS microbiology letters - Federation of European Microbiological Societies v. 106 (2): p. 211-216; 1993 Jan15. Includes references.

Language: English

Descriptors: Escherichia coli; Pseudomonas putida; Pseudomonas aeruginosa; Soil bacteria; Soil pollution; Biphenyl; Oxygenases; Plasmids; Cloning; Genetic transformation; Plasmid vectors; Gene expression

Abstract: A 6.5-kb EcoRI fragment containing the gene encoding 2,3-dihydroxybiphenyl dioxygenase from the plasmid pBS312 was cloned into broad host range plasmid RSF1010 and expressed in Escherichia coli, Pseudomonas putida and Pseudomonas aeruginosa strains. The increased expression of the gene was orientation-dependent and probably due to the transcription read through from the streptomycin promoter of the vector. Subcloning experiments of the PstI fragments of pBS312 plasmid using vector pBR322 revealed that the bphC gene encoding 2,3-dihydroxybiphenyl dioxygenase is localized on the 2.1-kb fragment. In Escherichia coli JM109, transformed by the plasmid pBS314 carrying the 2.1-kb insert in orientation which allowed expression of the bphC gene from the ampicillin promoter of pBR322, the enzyme activity of 2,3-dihydroxybiphenyl dioxygenase was ten times higher than that in parental strain Pseudomonas putida SU83. The results presented show the first case of the increased expression of Pseudomonas degradative gene in Escherichia coli.

109 NAL Call. No.: 448.3 AP5 Influence of 2,4,6-trinitrotoluene (TNT) concentration on the degradation of TNT in explosive-contaminated soils by the white rot fungus Phanerochaete chrysosporium.
Spiker, J.K.; Crawford, D.L.; Crawford, R.L. Washington, D.C. : American Society for Microbiology; 1992 Sep. Applied and environmental microbiology v. 58 (9): p. 3199-3202; 1992 Sep. Includes references.

Language: English

Descriptors: Soil pollution; Pollutants; Toluene; Explosives; Biodegradation; Phanerochaete chrysosporium

Abstract: The ability of Phanerochaete chrysosporium to bioremediate TNT (2,4,6-trinitrotoluene) in a soil containing 12,000 ppm of TNT and the explosives RDX (hexahydro-1,3,5-trinitro-1,3,5-triazine; 3,000 ppm) and HMX (octahydro-1,3,5,7-tetranitro-1,3,5,7-tetrazocine; 300 ppm) was investigated. The fungus did not grow in malt extract broth containing more than 0.02% (wt/vol; 24 ppm of TNT) soil. Pure TNT or explosives extracted from the soil were degraded by P. chrysosporium spore-inoculated cultures at TNT concentrations of up to 20 ppm. Mycelium-inoculated cultures degraded 100 ppm of TNT, but further growth was inhibited above 20 ppm. In malt extract broth, spore-inoculated cultures mineralized 10% of added [14C]TNT (5 ppm) in 27 days at 37 degrees C. No mineralization occurred during [14C]TNT biotransformation by mycelium-inoculated cultures, although the TNT was transformed.

110 NAL Call. No.: S592.7.A1S6 Influence of soil inoculum and redox potential on the degradation of several pyridine derivatives.
Kaiser, J.P.; Bollag, J.M.
Exeter : Pergamon Press; 1992 Apr.
Soil biology and biochemistry v. 24 (4): p. 351-357; 1992 Apr. Includes references.

Language: English

Descriptors: Indiana; South Carolina; Soil flora; Microbial degradation; Pyridines; Derivatives; Transformation; Redox potential; Contaminants; Exposure; Enrichment; Polluted soils; Surface layers; Anaerobic conditions; Aerobic treatment; Biological activity in soil; Biochemical pathways; Oxygen; Nitrate; Sulfate; Reduction; Denitrification; Persistence; Contamination

Abstract: The potential of four different soils to degrade several pyridine derivatives under aerobic and anaerobic conditions was investigated. There was little difference observed in the metabolic potential of unpolluted surface and unpolluted subsurface soils used as inocula from the same area. Under aerobic conditions, pyridine and hydroxylated pyridines were more rapidly transformed than the methylated pyridine derivatives. Under anaerobic conditions, none of the methylated or hydroxylated pyridine derivatives was completely degraded in 3 months by the unpolluted soil inocula. In using surface and subsurface soils which had been exposed to these compounds for several decades, all pyridine derivatives tested were biotransformed within 2 weeks in the presence of oxygen. However, under anaerobic conditions longer exposure was required. In the presence of sulfate, 3- and 4-picoline and 2- and 4-hydroxypyridine disappeared completely within 3 months when exposed to subsurface soil. On the other hand, the dimethylated and trimethylated pyridine derivatives were only partially transformed during this exposure period. Some of the heterocyclic compounds behaved quite differently when exposed to soil in the presence of either nitrate or sulfate under anaerobic conditions, indicating that the available electron acceptor influences the rate at which certain compounds are transformed.

111 NAL Call. No.: 448.3 AP5 Influence of the endogenous storage lipid poly-beta-hydroxybutyrate on the reducing power availability during cometabolism of trichloroethylene and naphthalene by resting methanotrophic mixed cultures. Henrysson, T.; McCarty, P.L.
Washington, D.C. : American Society for Microbiology; 1993 May. Applied and environmental microbiology v. 59 (5): p. 1602-1606; 1993 May. Includes references.

Language: English

Descriptors: Anaerobes; Trichloroethylene; Naphthalene; Oxidation; Microbial degradation; Metabolism; Polyhydroxybutyrate; Oxygenases; Enzyme activity; Bioremediation; Groundwater pollution

Abstract: The role of the storage lipid poly-beta-hydroxybutyrate (PHB) in trichloroethylene transformation by methanotrophic mixed cultures was investigated. Naphthalene oxidation rates were used to assay for soluble methane monooxygenase activity. The PHB content of methanotrophic cells grown in reactors varied diurnally as well as from day to day. A positive correlation between the amount of PHB in the cells and the naphthalene oxidation rate as well as between PHB and the trichloroethylene transformation rate and capacity was found. Addition of beta-hydroxybutyrate increased the naphthalene oxidation rates significantly. PHB content in cells could be manipulated by incubation at different methane-to-nitrogen ratios. A positive correlation between the naphthalene oxidation rate and the PHB content after these incubations could be seen. Both the PHB content and the naphthalene oxidation rates decreased with time in resting methanotrophic cells exposed to oxygen. However, this decrease in the naphthalene oxidation rate cannot be explained by the decrease in the PHB content alone. Probably a deactivation of the methane monooxygenase itself is also involved.

112 NAL Call. No.: 448.3 Ap5 Initial-phase optimization for bioremediation of munition compound-contaminated soils.
Funk, S.B.; Roberts, D.J.; Crawford, D.L.; Crawford, R.L. Washington : American Society for Microbiology; 1993 Jul. Applied and environmental microbiology v. 59 (7): p. 2171-2177; 1993 Jul. Includes references.

Language: English

Descriptors: Explosives; Organic nitrogen compounds; Azines; Azo compounds; Soil pollution; Polluted soils; Bioremediation; Microbial degradation; Soil ph; Anaerobic conditions; Mineralization

Abstract: We examined the bioremediation of soils contaminated with the munition compounds 2,4,6-trinitrotoluene (TNT), hexahydro-1,3,5-trinitro-1,3,5-triazine, and octahydro-1,3,5,7-tetranitro-1,3,5,7-tetraazocine by a procedure that produced anaerobic conditions in the soils and promoted the biodegradation of nitroaromatic contaminants. This procedure consisted of flooding the soils with 50 millimole phosphate buffer, adding starch as a supplemental carbon substrate, and incubating under static conditions. Aerobic heterotrophs, present naturally in the soil or added as an inoculum, quickly removed the oxygen from the static cultures, creating anaerobic conditions. Removal of parent TNT molecules from the soil cultures by the strictly anaerobic microflora occurred within 4 days. The reduced intermediates formed from TNT and hexahydro-1,3,5-trinitro-1, 3,5-triazine were removed from the cultures within 24 days, completing the first stage of remediation. The procedure was effective over a range of incubation temperatures, 20 to 37 degrees C, and was improved when 25 millimole ammonium was added to cultures buffered with 50 millimole potassium phosphate. Ammonium phosphate buffer (50 millimole), however, completely inhibited TNT reduction. The optimal pH for the first stage of remediation was between 6.5 and 7.0. When soils were incubated under aerobic conditions or under anaerobic conditions at alkaline pHs, the TNT biodegradation intermediates polymerized. Polymerization was not observed at neutral to slightly acidic pHs under anaerobic conditions. Completion of the first stage of remediation of munition compound-contaminated soils resulted in aqueous supernatants that contained no munition residues or aminoaromatic compounds.

113 NAL Call. No.: QR97.X46B56 Interactions of bacteria with cadmium.
Ron, E.Z.; Minz, D.; Finkelstein, N.P.; Rosenberg, E. Dordrecht, The Netherlands. : Kluwer Academic Publishers; 1992. Biodegradation v. 3 (2/3): p. 161-170; 1992. In the Special Issue: Microorganisms to Combat Pollution / edited by E. Rosenberg. Paper presented at an International Workshop on the "Use of Microorganisms to Combat Pollution," May 10-18, 1992, Israel. Includes references.

Language: English

Descriptors: Cadmium; Soil pollution; Water pollution; Bacteria; Strains; Bioremediation; Binding; Heavy metals; Biomass; Ph

114 NAL Call. No.: QH301.I54 International biodeterioration & biodegradation. Barking, Essex, England : Elsevier Science Publishers, c1992-; 1992-9999. v. : ill. ; 24 cm. On t.p. ampersand is in background of title.

Language: English; English

Descriptors: Biodegradation; Bioremediation

115 NAL Call. No.: TD192.5.I5 1991 International symposium environmental biotechnology 22-25 April 1991, Oostende, Belguim.
Verachtert, H.; Verstraete, W.
European Environmental Research Organisation, Commission of the European Communities
Belguim : Koninklijke Vlaamse Ingenieursvereniging,; 1991. 2 v. (722 p.) : ill. ; 30 cm. Includes bibliographical references.

Language: English

Descriptors: Environmental biotechnology

116 NAL Call. No.: TP248.27.M53W672 1992 Introduction to microbial biotechnology including hazardous waste treatment. Worne, Howard E.
Greenbelt, Md. : Hazardous Materials Control Resources Institue,; 1992. x, 231 p. : ill. ; 24 cm. Includes bibliographical references (p. 226-231).

Language: English

Descriptors: Microbial biotechnology; Hazardous substances

117 NAL Call. No.: 442.8 B5236 Metabolism and detoxification of TNT by Phanerochaete chrysosporium. Stahl, J.D.; Aust, S.D.
Orlando, Fla. : Academic Press; 1993 Apr30. Biochemical and biophysical research communications v. 192 (2): p. 477-482; 1993 Apr30. Includes references.

Language: English

Descriptors: Phanerochaete chrysosporium; Mycelium; Toluene; Concentration; Toxicity; Metabolic detoxification; Reduction; Mineralization; Microbial degradation; Nitrogen; Nutrient deficiencies; Lignin; Peroxidases; Ligninolytic microorganisms; Bioremediation

Abstract: Several lines of evidence suggest that TNT detoxification by Phanerochaete chrysosporium is through reduction. Rates of TNT reduction were directly correlated with mycelial mass and TNT concentration. Toxicity was inversely related to the amount of fungus. TNT toxicity was identical in both ligninolytic and nonligninolytic cultures. Rapid disappearance of the reduced metabolites coincided with production of the manganese-dependent peroxidases and mineralization of TNT was not observed until the lignin peroxidases were detected.

118 NAL Call. No.: 56.8 J822 Methods to assess the water quality impact of a restored riparian wetland. Vellidis, G.; Lowrance, R.; Smith, M.C.; Hubbard, R.K. Ankeny, Iowa : Soil and Water Conservation Society of America; 1993 May. Journal of soil and water conservation v. 48 (3): p. 223-230; 1993 May. Includes references.

Language: English

Descriptors: Georgia; Water pollution; Animal wastes; Bioremediation; Water quality; Runoff; Riparian forests; Wetlands; Reclamation; Pollution control

119 NAL Call. No.: RA1270.P35A1 Microbial abudance and degradation of polycyclic aromatic hydrocarbons in soil.
Mahmood, S.K.; Rao, P.R.
New York, N.Y. : Springer-Verlag; 1993 Apr. Bulletin of environmental contamination and toxicology v. 50 (4): p. 486-491; 1993 Apr. Includes references.

Language: English

Descriptors: Soil pollution; Polycyclic hydrocarbons; Phenanthrene; Soil fungi; Soil bacteria; Microbial degradation; Bioremediation

120 NAL Call. No.: TD192.5.S63 1992 Microbial control of pollution.
Fry, John C.
Society for General Microbiology. Symposium. 1992 : University of Cardiff) Cambridge [England] ; New York, NY, USA : Cambridge University Press,; 1992. xii, 343 p. : ill. ; 24 cm. Forty-eighth Symposium of the Society for General Microbiology, held at the University of Cardiff, March 1992. Published for the Society of General Microbiology. Includes bibliographical references and index.

Language: English

Descriptors: Environmental biotechnology

121 NAL Call. No.: 448.3 AP5 Microbial populations and hydrocarbon biodegradation potentials in fertilized shoreline sediments affected by the T/V Exxon Valdez oil spill. Lindstrom, J.E.; Prince, R.C.; Clark, J.C.; Grossman, M.J.; Yeager, T.R.; Braddock, J.F.; Brown, E.J.
Washington, D.C. : American Society for Microbiology; 1991 Sep. Applied and environmental microbiology v. 57 (9): p. 2514-2522; 1991 Sep. Includes references.

Language: English

Descriptors: Alaska; Nitrogen-phosphorus fertilizers; Microbial degradation; Oil spills; Hydrocarbons; Mineralization

Abstract: The effort to clean up the T/V Exxon Valdez oil spill in Prince William Sound, Alaska, included the use of fertilizers to accelerate natural microbial degradation of stranded oil. A program to monitor various environmental parameters associated with this technique took place during the summer of 1990. Microbiological assays for numbers of heterotrophic and oil-degrading microbes and their hydrocarbon mineralization potentials were performed in support of this program. Fertilizer addition resulted in higher hexadecane and phenanthrene mineralization potentials on treated plots than on untreated reference plots. Microbial numbers in treated and reference surface sediments were not significantly different immediately after the first nutrient application in May 1990. However, subsurface sediments from treated plots had higher numbers of hydrocarbon degraders than did reference sediments shortly after treatment. The second application of fertilizer, later in summer, resulted in surface and subsurface increases in numbers of hydrocarbon degraders with respect to reference sediments at two of the three study sites. Elevated mineralization potentials, coupled with increased numbers of hydrocarbon degraders, indicated that natural hydrocarbon biodegradation was enhanced. However, these microbiological measurements alone are not sufficient to determine in situ rates of crude oil biodegradation.

122 NAL Call. No.: QH540.J6 Microbial release of 2,4-dichlorophenol bound to humic acid or incorporated during humification.
Dec, J.; Shuttleworth, K.L.; Bollag, J.M. Madison, Wis. : American Society of Agronomy; 1990 Jul. Journal of environmental quality v. 19 (3): p. 546-551; 1990 Jul. Includes references.

Language: English

Descriptors: Humic acids; 2,4-dichlorophenol; Pollutants; Soil flora; Microbial activities; Humification; Mineralization; Polymerization; Binding; Soil pollution; Bioremediation

Abstract: The microbial release of 14C-labeled 2,4-dichlorophenol (DCP) bound to synthetic and natural humic materials or polymerized by enzymes was investigated to evaluate the possibility of future adverse effects if binding or polymerization is used for decontamination purposes. After 12 wk of incubation with microorganisms obtained from a forest soil, the amounts of substances released into the media were very small (maximum 2.2% of the initially bound 14C) without regard to the kind of the polymer into which 14C-DCP was incorporated. Most of the radioactivity (46.2 to 80.8%) remained bound to the precipitated humic materials or in the DCP-polymer (90.1 to 97.0%). Certain amounts of the released substances evolved in the form of 14CO2 (1.0 to 9.4% from humic materials and 0 to 0.5% from a DCP-polymer). The rate of mineralization differed depending on the type of DCP binding-surface-bound or incorporated during synthesis of humic acid-and on the kind of polymer to which 14C-DCP was attached. The release into the media and 14CO2 evolution for synthetic and natural humic acids was essentially the same. When only DCP was present in the growth medium, the formation of 14CO2 was less than from a DCP-humic acid complex; this may indicate that 14CO2 from a DCP-humic acid complex originated mostly from DCP derivatives. The data obtained for DCP did not provide any evidence for a delayed pollution problem associated with polymerization or binding of xenobiotics to humic acids.

123 NAL Call. No.: TA166.T72 Microbial treatment of metal pollution--a working biotechnology?. Gadd, G.M.; White, C.
Cambridge : Elsevier Science Publishing Co; 1993 Aug. Trends in biotechnology v. 11 (8): p. 353-359; 1993 Aug. In the special issue: Bioremediation: technological and commercial issues in the biological detoxification of polluted sites. Includes references.

Language: English

Descriptors: Heavy metals; Pollutants; Radionuclides; Microbial activities; Treatment; Biotechnology; Pollution control

Abstract: Some of the main processes that remove, immobilize or detoxify heavy metals and radionuclides in the natural environment result from microbial activities. These activities can be harnessed to clean up toxic metal wastes before they enter the wider environment. To date, the most successful biotechnological processes utilize biosorption and bioprecipitation, but other processes such as binding by specific macromolecules may have future potential. Technologies using these processes are currently used to control pollution from diverse sources, including smelters and mine workings.

124 NAL Call. No.: TP248.13.C74 Microbiological and biotechnological aspects of metabolism of carbamates and organophosphates.
Chapalamadugu, S.; Chaudhry, G.R.
Boca Raton, Fla. : CRC Press; 1992.
Critical reviews in biotechnology v. 12 (5/6): p. 357-389; 1992. Includes references.

Language: English

Descriptors: Pesticide residues; Environmental degradation; Carbamate pesticides; Organophosphorus pesticides; Mineralization; Microbial degradation; Metabolism; Biochemical pathways; Genetics; Genes

125 NAL Call. No.: 448.3 Ap5 Microcosm and in situ field studies of enhanced biotransformation of trichloroethylene by phenol-utilizing microorganisms. Hopkins, G.D.; Semprini, L.; McCarty, P.L. Washington : American Society for Microbiology; 1993 Jul. Applied and environmental microbiology v. 59 (7): p. 2277-2285; 1993 Jul. Includes references.

Language: English

Descriptors: Aerobes; Bacteria; Microbial degradation; Trichloroethylene; Phenol; Metabolism; Metabolites; Chlorinated hydrocarbons; Bioremediation; Groundwater pollution; Aquifers; Toluene

Abstract: The ability of different aerobic groundwater microorganisms to cometabolically degrade trichloroethylene (TCE), 1,2-cis-dichloroethylene (c-DCE), and 1,2-trans-dichloroethylene (t-DCE) was evaluated both in groundwater-fed microcosms and in situ in a shallow aquifer. Microcosms amended with phenol or toluene were equally effective in removing c-DCE (> 90%) followed by TCE (60 to 70%), while the microcosm fed methane was most effective in removing t-DCE (> 90%). The microcosm fed ammonia was the least effective. None of the microcosms effectively degraded 1,1,1-trichloroethane. At the Moffett Field groundwater test site, in situ removal of c-DCE and TCE coincided with biostimulation through phenol and oxygen injection and utilization, with c-DCE removed more rapidly than TCE. Greater TCE and c-DCE removal was observed when the phenol concentration was increased. Over 90% removal of c-DCE and TCE was observed in the 2-m biostimulated zone. This compares with 40 to 50% removal of c-DCE and 15 to 25% removal of TCE achieved by methane-grown microorganisms previously evaluated in an adjacent in situ test zone. The in situ removal with phenol-grown microorganisms agrees qualitatively with the microcosm studies, with the rates and extents of removal ranked as follows: c-DCE > TCE > t-DCE. These studies demonstrate the potential for in situ TCE bioremediation using microorganisms grown on phenol.

126 NAL Call. No.: 448.3 Ap5 Mineralization of the s-triazine ring of atrazine by stable bacterial mixed cultures.
Mandelbaum, R.T.; Wackett, L.P.; Allan, D.L. Washington : American Society for Microbiology; 1993 Jun. Applied and environmental microbiology v. 59 (6): p. 1695-1701; 1993 Jun. Includes references.

Language: English

Descriptors: Atrazine; Microbial degradation; Soil bacteria; Polluted soils; Metabolites; Metabolism; Bioremediation

Abstract: Enrichment cultures containing atrazine (2-chloro-4-ethylamino-6-isopropylamino-1,3,5-triazine) at a concentration of 100 ppm (0.46 mM) as a sole nitrogen source were obtained from soils exposed to repeated spills of atrazine, alachlor, and metolachlor. Bacterial growth occurred concomitantly with formation of metabolites from atrazine and subsequent biosynthesis of protein. When ring-labeled [14C]atrazine was used, 80% or more of the s-triazine ring carbon atoms were liberated as 14 CO2. Hydroxyatrazine may be an intermediate in the atrazine mineralization pathway. More than 200 pure cultures isolated from the enrichment cultures failed to utilize atrazine as a nitrogen source. Mixing pure cultures restored atrazine-mineralizing activity. Repeated transfer of the mixed cultures led to increased rates of atrazine metabolism. The rate of atrazine degradation, even at the elevated concentrations used, far exceeded the rates previously reported in soils, waters, and mixed and pure cultures of bacteria.

127 NAL Call. No.: TD403.G7 Model development and simulation of bioremediation in soil beds with aggregates.
Dhawan, S.; Erickson, L.E.; Fan, L.T.
Dublin, Ohio : Ground Water Pub. Co; 1993 Mar. Ground water v. 31 (2): p. 271-284; 1993 Mar. Includes references.

Language: English

Descriptors: Soil pollution; Groundwater pollution; Organic compounds; Biodegradation; Simulation models; Soil; Aggregates

Abstract: One method of remediating contaminated soil and ground water is through management of the subsurface environment so that indigenous microorganisms can biodegrade organic contaminants. Modeling and simulation offer promising means of assessing the migration and attenuation of such contaminants being treated in situ in the subsurface. In this paper, a macropore flow model has been developed to account for bioremediation in the interstitial spaces among soil aggregates. This model has been combined with another bioremediation model which accounts for diffusion and biodegradation in the micropores and soil particles in the aggregates. The combined model comprises a system of six coupled equations, of which three are nonlinear ordinary differential equations and three are nonlinear partial differential equations. Dimensional analysis of these equations has yielded useful dimensionless parameters for evaluating the relative significance of each mechanism in remediation. Numerical experiments have been conducted to evaluate the effects of initial contaminant concentration, aggregate size, and soil-water partition factor. The total time of remediation has been found to depend on the rate at which contaminants are consumed within the large aggregates which, in turn, depends on the biodegradation kinetics and the rates of diffusion of substrate and oxygen in the aggregates. For soil with aggregates whose radius is 1 cm or larger, the results of simulation indicate that the remediation time for the aggregates is significantly longer compared to the corresponding result for homogeneous soil. For contaminants with large partition coefficients, the estimated time for remediation achieved through microbial oxidation in situ is much shorter than that achieved through purely diffusional transport of the contaminants out of the soil bed.

128 NAL Call. No.: TA166.T72 Monitoring the efficacy of bioremediation. Heitzer, A.; Sayler, G.S.
Cambridge : Elsevier Science Publishing Co; 1993 Aug. Trends in biotechnology v. 11 (8): p. 334-343; 1993 Aug. In the special issue: Bioremediation: technological and commercial issues in the biological detoxification of polluted sites. Includes references.

Language: English

Descriptors: Toxic substances; Detoxification; Waste treatment; Pollution control; Bioremediation; Efficiency; Monitoring; Chemistry; Molecular biology; Techniques

Abstract: The general acceptance of bioremediation technology as an environmentally sound and economic treatment for hazardous waste requires the demonstration of its efficacy, reliability and predictability, as well as its advantages over conventional treatments. An effective monitoring design includes protocols for treatment-specific, representative sampling, control and monitoring: these should take into account abiotic and biotic pollutant fate processes in all relevant process compartments. A number of well-established and novel chemical and molecular biological monitoring techniques and parameters are available. Logical and balanced combinations of both chemical and biological monitoring parameters should be used to demonstrate complete degradation and detoxification of a hazardous waste as well as the biological nature of the process. At each process-scale level, a set of general criteria should be used for a systematic evaluation of the overall efficacy of bioremediation.

129 NAL Call. No.: QR1.F44 Oligomers of 4-chloroaniline are intermediates formed during its biodegradation by Phanerochaete chrysosporium. Chang, C.W.; Bumpus, J.A.
Amsterdam : Elsevier Science Publishers; 1993 Mar01. FEMS microbiology letters - Federation of European Microbiological Societies v. 107 (2/3): p. 337-342; 1993 Mar01. Includes references.

Language: English

Descriptors: Phanerochaete chrysosporium; Herbicides; Organic nitrogen compounds; Metabolites; Oxidation; Lignin; Peroxidases; Microbial degradation; Bioremediation; Soil pollution

Abstract: Lignin peroxidase H2 (LP-H2) from Phanerochaete chrysosporium oxidized 4-chloroaniline to form several oligomers. Included among the compounds identified were: 4,4'-dichloroazobenzene, 2-(4-chloroanilino)-5-hydroxybenzoquinone-di-4-chloroanil and 2-amino-5-(4-chloroanilino) benzoquinone-di-4-chloroanil. In contrast to results by others, we showed that oligomers of 4-chloroaniline were also formed by the fungus in vivo. It was also demonstrated that, although these potentially toxic intermediates are made, they are also degraded.

130 NAL Call. No.: TD192.5.O57 1991 On-site bioreclamation processes for xenobiotic and hydrocarbon treatment. Hinchee, Robert E.; Olfenbuttel, Robert F. Boston : Butterworth-Heinemann,; 1991.
xviii, 539 p. : ill. ; 25 cm. Selected papers from the international symposium "In Situ and On-Site Bioreclamation" held in San Diego in March of 1991. Includes bibliographical references and index.

Language: English

Descriptors: Bioremediation; Xenobiotics; Hydrocarbons

131 NAL Call. No.: NBUTD192.5 O57 1991 On-site bioreclamation processes for xenobiotic and hydrocarbon treatment. Hinchee, Robert E.; Olfenbuttel, Robert F. Boston : Butterworth-Heinemann,; 1991.
xviii, 539 p. : ill. ; 25 cm. Selected papers from the international symposium "In Situ and On-Site Bioreclamation" held in San Diego in March of 1991. Includes bibliographical references and index.

Language: English

Descriptors: Bioremediation; Xenobiotics; Hydrocarbons

132 NAL Call. No.: S592.7.A1S6 Parathion degradation by a Pseudomonas sp. and a Xanthomonas sp. and by their crude enzyme extracts as affected by some cations. Tchelet, R.; Levanon, D.; Mingelgrin, U.; Henis, Y. Exeter : Pergamon Press; 1993 Dec.
Soil biology & biochemistry v. 25 (12): p. 1665-1671; 1993 Dec. Includes references.

Language: English

Descriptors: Parathion; Biodegradation; Hydrolysis; Xanthomonas; Pseudomonas; Metal ions; Cations; Bioremediation; Polluted soils

Abstract: A Pseudomonas sp. and a Xanthomonas sp. were isolated from a pesticide disposal site in northern Israel. Both degraded parathion in two stages. In the first stage, p-nitrophenol (PNP) was released by a parathion hydrolase, while in the second stage PNP was degraded.The effect of Cu2+, Fe2+, Ca2+, Mn2+, Al3+, Zn2+ and NaEDTA on parathion hydrolysis to PNP by growing cultures and by crude enzyme extracts of the isolates was studied. Parathion hydrolysis by both either living cells or crude enzyme extracts of the Pseudomonas sp. was inhibited by Cu2+ even at a concentration of 20 micromoles l-1, as opposed to this cation's stimulatory effect on the degradation of parathion by the Xanthomonas sp. Other cations investigated had a smaller effect on the rate of degradation by either bacterium. NaEDTA strongly inhibited parathion hydrolysis in the living cells, but not in the crude enzyme extracts of the Pseudomonas sp. In contrast, NaEDTA inhibited parathion hydrolysis in either living cells or crude enzyme extracts of the Xanthomonas sp.

133 NAL Call. No.: TD420.A1E5 Performance standards for in situ bioremediation. MacDonald, J.A.; Rittmann, B.E.
Washington, D.C. : American Chemical Society; 1993 Oct. Environmental science & technology v. 27 (10): p. 1974-1979; 1993 Oct. Includes references.

Language: English

Descriptors: Groundwater pollution; Soil pollution; Bioremediation; Biological activity in soil; Microorganisms

134 NAL Call. No.: QH442.J69 Phenoloxidases and hydrolases from Pycnoporus sanguineus (UEC-2050 strain): applications.
Esposito, E.; Innocentini-Mei, L.H.; Ferraz, A.; Canhos, V.P.; Duran, N. Amsterdam : Elsevier Science Publishers B.V.; 1993 Jun. Journal of Biotechnology v. 29 (3): p. 219-220; 1993 Jun. Includes references.

Language: English

Descriptors: Pycnoporus sanguineus; Peroxidases; Beta-glucosidase; O-glycoside hydrolases; Monophenol monooxygenase; Laccase; Enzyme activity; Bioremediation; Microbial degradation; Pulp mill effluent; Decolorization; Kraft mill effluent

135 NAL Call. No.: QD1.A45 Photochemical and microbial degradation technologies to remove toxic chemicals.
Matsumura, F.; Katayama, A.
Washington, D.C. : American Chemical Society, 1974-; 1992. ACS symposium series (510): p. 201-209; 1992. In the series analytic: Pesticide Waste Management: technology and regulation / edited by J.B. Bourke, A.S. Felsot, T.J. Gilding, J.K. Jensen, J.N. Seiber. Includes references.

Language: English

Descriptors: Pollutants; Toxic substances; Chlorinated hydrocarbons; Aromatic compounds; Microbial degradation; Photolysis; Ultraviolet radiation; Phanerochaete chrysosporium; Strains; Decay fungi; Bioremediation

136 NAL Call. No.: 448.3 AP5 Physiological factors affecting carbon tetrachloride dehalogenation by the denitrifying bacterium Pseudomonas sp. strain KC. Lewis, T.A.; Crawford, R.L.
Washington, D.C. : American Society for Microbiology; 1993 May. Applied and environmental microbiology v. 59 (5): p. 1635-1641; 1993 May. Includes references.

Language: English

Descriptors: Pseudomonas; Denitrifying microorganisms; Carbon tetrachloride; Chemical reactions; Microbial degradation; Regulation; Ferrous ions; Ferric ions; Cobalt; Metal ions; Iron hydroxides; Bioremediation; Groundwater pollution; Aquifers; Denitrification

Abstract: Pseudomonas sp. strain KC was grown on a medium with a low content of transition metals in order to examine the conditions for carbon tetrachloride (CT) transformation. Several carbon sources, including acetate, glucose, glycerol, and glutamate, were able to support CT transformation. The chelators 2,2'-dipyridyl and 1,10-phenanthroline stimulated CT transformation in a rich medium that otherwise did not support this activity. Low (<10 micromolar) additions of dissolved iron(II), iron(III), and cobalt(II), as well as an insoluble iron(III) compound, ferric oxyhydroxide, inhibited CT transformation. The addition of 50 micromolar iron to actively growing cultures resulted in delayed inhibition of CT transformation. CT transformation was seen in aerobic cultures of KC, but with reduced efficiency compared with denitrifying cultures. Inhibition of CT transformation by iron was also seen in aerobically grown cultures. Optimal conditions were used in searching for effective CT transformation activity among denitrifying enrichments grown from samples of aquifer material. No activity comparable to that of Pseudomonas sp. strain KC was found among 16 samples tested.

137 NAL Call. No.: QK725.I43 Phytochelatin-mediated cadmium tolerance in Schizosaccharomyces pombe. Ow, D.W.
Columbia, MD : Tissue Culture Association, c1991-; 1993 Oct. In vitro cellular & developmental biology. Plant : journal of the Tissue Culture Association v. 29P (4): p. 213-219; 1993 Oct. Paper presented at the "Session-in-Depth Bioremediation through Biotechnological Means" at the 1993 Congress on Cell and Tissue Culture, June 5-9, 1993, San Diego, California. Includes references.

Language: English

Descriptors: Endomycetales; Peptides; Binding proteins; Cadmium; Metal tolerance; Mutants; Tonoplast; Vacuoles; Uptake; Ligases; Carboxy-lyases; Enzyme activity; Purines; Biosynthesis

138 NAL Call. No.: Q1.D57 Poison eaters.
Chollar, S.
Los Angeles, Calif. : Time, Inc. :.; 1990 Apr. Discover v. 11 (4): p. 76-78; 1990 Apr.

Language: English

Descriptors: Flavobacterium; Waste treatment; Aquatic environment; Pesticides

139 NAL Call. No.: TD192.5.K56 1992 Practical environmental bioremediation. King, R. Barry; Long, Gilbert M.; Sheldon, John K. Boca Raton : Lewis Publishers,; 1992.
149 p. : ill. ; 25 cm. Includes bibliographical references and index.

Language: English

Descriptors: Bioremediation

140 NAL Call. No.: TD426.N95 1993 Practical techniques for groundwater and soil remediation. Nyer, Evan K.
Boca Raton : Lewis Publishers,; 1993.
214 p. : ill. ; 25 cm. (Geraghty & Miller science and engineering series). Includes bibliographical references and index.

Language: English

Descriptors: Water, Underground; Soil pollution; Bioremediation

141 NAL Call. No.: TP248.13.C74 Principles of biotechnological treatment of industrial wastes. Roig, M.G.; Rodriguez, M.J.M.; Cachaza, J.M.; Sanchez, L.M.; Kennedy, J.F. Boca Raton, Fla. : CRC Press,; 1993.
Critical reviews in biotechnology v. 13 (2): p. 99-116; 1993. Includes references.

Language: English

Descriptors: Industrial wastes; Waste water; Biological treatment; Pollution; Biotechnology; Reviews

142 NAL Call. No.: QR82.P78P82 1992 Pseudomonas molecular biology and biotechnology. Galli, Enrica; Silver, S.; Witholt, Bernard Federation of European Microbiological Societies Washington, D.C. : American Society for Microbiology,; 1992. xii, 443 p. : ill. ; 26 cm. "Based on the proceedings of a symposium held under the auspices of the Federation of European Microbiological Societies from June 16 to June 20, 1991, in Trieste, Italy"--T.p. verso. Includes bibliographical references and indexes.

Language: English

Descriptors: Pseudomonas; Biotechnology

143 NAL Call. No.: QR1.E9 Rapid anaerobic mineralization of pyridine in a subsurface sediment inoculated with a pyridine-degrading Alcaligenes sp. Ronen, Z.; Bollag, J.M.
Berlin ; New York : Springer International, [1984?-; 1992 May. Applied microbiology and biotechnology v. 37 (2): p. 264-269; 1992 May. Includes references.

Language: English

Descriptors: Alcaligenes; Pyridines; Anaerobic conditions; Mineralization; Industrial microbiology

Abstract: A denitrifying bacterium capable of pyridine mineralization under anaerobic conditions was isolated from polluted soil. The bacterium, identified as Alcaligenes sp., was used in inoculation experiments. A subsurface sediment from a polluted site was amended with 10 micrograms/g (14)C-labeled pyridine, and 250 micrograms/g nitrate, and then inoculated with the bacterium at an inoculum size of 4.5 X 10(7) cells/g. After 44 h incubation at 28 degrees C under anaerobic conditions, 67% of the radioactivity was recovered as (14)CO2: 2% was extracted with 50% methanol, and 24% was recovered by combustion of the sediment. Analysis of the methanol extract revealed that no pyridine could be detected in the inoculated sediment. In contrast, mineralization of pyridine by the native microflora in the sediment occurred much more slowly: after 7 days of incubation only 10% of the added radioactivity was recovered as (14)CO2. At an inoculum size of 2 X 10(3) cells/g pyridine mineralization was not as effective as at an inoculum size of 2 X 10(7) cells/g. It is presumed that suppression of the introduced bacteria by the native microflora of the sediment prevents degradation at a low inoculum size. Amending the sediment with nitrate and phosphate improved pyridine mineralization by the introduced bacterium. These findings demonstrate the feasibility of using soil inoculation anaerobically for the bioremediation of pyridine-polluted soils.

144 NAL Call. No.: 47.8 Am33P Recent development in poultry waste digestion and feather utilization--a review.
Shih, J.C.H.
Champaign, IL : Poultry Science Association, 1921-; 1993 Sep. Poultry science v. 72 (9): p. 1617-1620; 1993 Sep. Includes references.

Language: English

Descriptors: Feathers; Anaerobic digesters; Poultry manure; Bacillus licheniformis; Proteinases; Feather meal; Digestibility; Feed additives; Literature reviews

Abstract: The intensive and large-scale production of food animals and animal products has generated an enormous waste disposal problem for the animal industry. These wastes, which include animal excreta, mortalities, hair, feathers, and processing wastes, are largely organic materials and are convertible to useful resources. Making the conversion processes efficient and economical presents a great challenge to modern biotechnology. An efficient thermophilic anaerobic digester system has been developed that converts animal manure to methane for an energy source, solid residues for feed supplements, and liquid nutrients for aquaculture. This digester system also destroys pathogens and thus protects environmental health. During the development of this system, a feather-degrading bacterium was discovered and identified as a thermophilic Bacillus licheniformis, Strain PWD-1. The bacterium can ferment and convert feathers to feather-lysate, a digestible protein source for feed use. An enzyme, keratinase, secreted by this bacterium was purified and characterized. This keratinase is a potent protease that hydrolyzes all proteins tested, including collagen, elastin, and feather keratin. When the enzyme was mixed as an additive in feed, it significantly enhanced the digestibility of feather meal in chickens. In addition to feed technology, the bacterium and the enzyme are believed to have many other industrial and environmental applications.

145 NAL Call. No.: QK725.I43 Remediation of contaminated soils with green plants: an overview. Cunningham, S.D.; Berti, W.R.
Columbia, MD : Tissue Culture Association, c1991-; 1993 Oct. In vitro cellular & developmental biology. Plant : journal of the Tissue Culture Association v. 29P (4): p. 207-212; 1993 Oct. Paper presented at the "Session-in-Depth Bioremediation through Biotechnological Means" at the 1993 Congress on Cell and Tissue Culture, June 5-9, 1993, San Diego, California. Includes references.

Language: English

Descriptors: Plants; Bioremediation; Pollutants; Uptake; Metabolic detoxification; Soil pollution; Polluted soils

146 NAL Call. No.: QD415.A1J62 Respirometric analysis of the biodegradation of organic contaminants in soil and water.
Graves, D.A.; Lang, C.A.; Leavitt, M.E. Totowa, N.J. : Humana Press; 1991.
Applied biochemistry and biotechnology v. 28/29: p. 813-826; 1991. Includes references.

Language: English

Descriptors: Soil pollution; Contaminants; Organic compounds; Bioremediation; Respiratory gases; Biochemical oxygen demand

147 NAL Call. No.: QR1.E9 Role of inoculum preparation and density on the bioremediation of 2,4-D-contaminated soil by bioaugmentation. Comeau, Y.; Greer, C.W.; Samson, R.
Berlin ; New York : Springer International, [1984?-; 1993 Feb. Applied microbiology and biotechnology v. 38 (5): p. 681-687; 1993 Feb. Includes references.

Language: English

Descriptors: Pseudomonas cepacia; Soil bacteria; Culture techniques; Soil inoculation

Abstract: The effect of inoculum preparation and density on the efficiency of remediation of 2,4-dichlorophenoxyacetic acid (2,4-D) by bioaugmentation was studied in non-sterile soil. A 2,4-D-degrading Pseudomonas cepacia strain (designated BRI6001) was used initially in liquid culture to determine the effects of pre-growth induction and of inoculum density. The time for complete 2,4-D degradation was reduced by 0.5 day for each log increase of inoculum density. In mixed (BRI6001 and soil bacteria) liquid cultures, a competition effect for 2,4-D became apparent at low inoculum levels (less than 10(5) cfu/ml BRI6001 for 10(8) cfu/ml soil bacteria) but only when the soil bacteria included indigenous 2,4-D degraders. In static non-sterile soil, the effect of inoculum density on 2,4-D degradation was comparable to that in liquid culture but only at high inoculation levels. At lower levels, a biological effect for 2,4-D degradation became apparent, as was observed in mixed liquid cultures, whereas at intermediate levels, a combination of biological, physical and chemical factors decreased the efficiency of bioaugmentation. The acclimation period for 2,4-D degradation in soil bioaugmented with BRI6001 reflected mainly the time required for cell induction and, presumably, for overcoming the physical limitation of diffusion of both 2,4-D and added bacteria in the soil matrix.

148 NAL Call. No.: 286.8 N488 Scientist using plants to clean up metals in contaminated soil. Bernstein, E.
New York, N.Y. : H.J. Raymond & Co. :.; 1992 Sep08. The New York times. p. B8; 1992 Sep08.

Language: English

Descriptors: Apocynum; Ambrosia; Genetic engineering; Waste treatment; Heavy metals

149 NAL Call. No.: QR97.X46B56 Selection and isolation of bacteria capable of degrading dinoseb (2-sec-butyl-4,6-dinitrophenol).
Stevens, T.O.; Crawford, R.L.; Crawford, D.L. Boston, Mass. : Kluwer Academic Publishers; 1991. Biodegradation v. 2 (1): p. 1-13; 1991. Includes references.

Language: English

Descriptors: Dinoseb; Soil bacteria; Microbial degradation; Transformation; Mineralization; Persistence; Anaerobic conditions; Enrichment; Isolation techniques; Soil pollution; Water pollution

150 NAL Call. No.: QR1.L47 Selective plating medium for enumeration and recovery of a hexachlorocyclohexane-degrading Pseudomonas Ptm+ strain from soil. Anu Appaiah, K.A.; Shaw, D.M.; Karanth, N.G.K. Oxford : Blackwell Scientific Publications; 1993 Jun. Letters in applied microbiology v. 16 (6): p. 287-290; 1993 Jun. Includes references.

Language: English

Descriptors: Pseudomonas; Introduced species; Chlorinated hydrocarbons; Microbial degradation; Soil pollution; Polluted soils; Isolation techniques; Culture media; Bacterial counting; Enumeration; Streptomycin; Drug resistance; Monitoring; Bioremediation

151 NAL Call. No.: 448.3 Ap5 A substrate-dependent biological containment system for Pseudomonas putida based on the Escherichia coli gef gene. Jensen, L.B.; Ramos, J.L.; Kaneva, Z.; Molin, S. Washington : American Society for Microbiology; 1993 Nov. Applied and environmental microbiology v. 59 (11): p. 3713-3717; 1993 Nov. Includes references.

Language: English

Descriptors: Pseudomonas putida; Escherichia coli; Structural genes; Bacterial proteins; Recombinant DNA; Genetic engineering; Transposable elements; Plasmid vectors; Microbial degradation; Bioremediation; Benzoates (esters); Inoculum; Introduced species; Polluted soils; Antibacterial properties

Abstract: A model substrate-dependent suicide system to biologically contain Pseudomonas putida KT2440 is reported. The system consists of two elements. One element carries a fusion between a synthetic lac promoter (P(A1-04/03) and the gef gene, which encodes a killing function. This element is contained within a transposaseless mini-Tn5 transposon so that it can be integrated at random locations on the Pseudomonas chromosome. The second element, harbored by plasmid pCC102, is designed to control the first and bears a fusion between the promoter of the P. putida TOL plasmid-encoded meta-cleavage pathway operon (Pm) and the lacI gene, encoding the Lac repressor, plus xylS2, coding for a positive regulator of Pm. In liquid culture under optimal growth conditions and in sterile and nonsterile soil microcosms, P. putida KT2440(pWWO) bearing the containment system behaves as designed. In the presence of a XylS effector, such as m-methylbenzoate, the LacI protein is synthesized, preventing the expression of the killing function. In the absence of effectors, expression of the P(A1-04/03)::gef cassette is no longer prevented and a high rate of cell killing is observed. Fluctuation test analyses revealed that mutants resistant to cell killing arise at a frequency of around 10-5 to 10-6 per cell per generation. Mutations are linked to the killing element rather than to the regulatory one. In bacteria bearing two copies of the killing cassette, the rate of appearance of mutants resistant to killing decreased to as low as 10-8 per cell per generation.

152 NAL Call. No.: QH545.A1C7 Subsurface contaminant bioremediation engineering. Tursman, J.F.; Cork, D.J.
Boca Raton, Fla. : CRC Press; 1992.
Critical reviews in environmental control v. 22 (1/2): p. 1-26; 1992. Literature review. Includes references.

Language: English

Descriptors: Soil pollution; Groundwater pollution; Pollutants; Halogenated hydrocarbons; Microbial degradation; Polluted soils; Chlorinated hydrocarbons; Literature reviews; Engineering; Soil flora; Subsurface layers

153 NAL Call. No.: QH545.A1C7 Subsurface, terrestrial microbial ecology and biodegradation of organic chemicals: a review.
Dobbins, D.C.; Aelion, C.M.; Pfaender, F. Boca Raton, Fla. : CRC Press; 1992.
Critical reviews in environmental control v. 22 (1/2): p. 67-136; 1992. Literature review. Includes references.

Language: English

Descriptors: Soil flora; Water microbiology; Groundwater; Community ecology; Biodegradation; Microbial degradation; Organic compounds; Adaptation; Environmental factors; Soil pollution; Groundwater pollution; Polluted soils; Literature reviews; Subsurface layers

154 NAL Call. No.: QR100.M5 Survival of 2,4-dichlorophenoxyacetic acid degrading Alcaligenes eutrophus AEO 106(pR0101) in lake water microcosms.
Kandel, A.; Nybroe, O.; Rasmussen, O.F. New York, N.Y. : Springer-Verlag; 1992. Microbial ecology v. 24 (3): p. 291-303; 1992. Includes references.

Language: English

Descriptors: Alcaligenes; Recombinant DNA; Survival; Microbial degradation; 2,4-d; Dosage effects; Aquatic environment; Lakes; Polluted water; Biological competition; Plasmids; Catabolism; Immunofluorescence; Immunoblotting; Dna hybridization

Abstract: Survival of the 2,4-dichlorophenoxyacetic acid (2,4-D) degrading Alcaligenes eutrophus strain AEO106 harboring the catabolic plasmid PRO101 was studied in lake water from the eutrophic lake Frederiksborg Slotsso. Survival experiments were performed for periods of 7 days in laboratory microcosms containing filtered (0.2-micrometer pore size) or natural lake water amended with increasing concentrations of 2,4-D. A. eutrophus AE0106 was detected by combining the fluorescent antibody method with selective and nonselective plating followed by colony blotting and colony hybridization. Comparison of colony blotting and colony hybridization demonstrated that the A. eutrophus AE0106 host organism and the catabolic plasmid pRO101 had similar fates in the model system employed. In all experiments culturable counts of A. eutrophus AE0106 were lower than fluorescent antibody counts and frequently a decline in culturable counts occurred at times when the fluorescent antibody method showed an increasing population size. Amendment with 2,4-D increased survival of A. eutrophus AE0106 both in filtered and in natural lake water. Survival was always poorer in model systems with natural water than in 0.2 micrometer-filtered water.

155 NAL Call. No.: QR1.C78 Survival of Alcaligenes xylosoxidans degrading 2,2-dichloropropionate and horizontal transfer of its halidohydrolase gene in a soil microcosm. Brokamp, A.; Schmidt, F.R.J.
New York, N.Y. : Springer International; 1991 May. Current microbiology v. 22 (5): p. 299-306; 1991 May. Includes references.

Language: English

Descriptors: Alcaligenes; Soil bacteria; Chlorthal-dimethyl; Microbial degradation; Plasmids; Survival; Growth; Substrates; Hydrolases; Enzyme activity; Pseudomonas fluorescens; Gene transfer; Soil pollution

Abstract: A soil microcosm, containing a mixture of sand and a well-characterized phaeozem soil from loess, was developed for biodegradative applications. It was inoculated with soil-borne Alcaligenes xylosoxidans AB IV, degrading 2,2-dichloropropionate (DCPA), by a plasmid-encoded haloalkanoic acid halidohydrolase. In long-term microcosm experiments, survival of Alcaligenes xylosoxidans ABIV in the presence and absence of selective pressure by the xenobiotic compound could be demonstrated as well as its capacity to maintain degradation of DCPA. At the same time its plasmid, pFL40, containing the degradative gene, dhlC, was horizontally transferred to Pseudomonas fluorescens in sterilized soil and also to different indigenous soil bacteria in nonsterilized soil.

156 NAL Call. No.: TP995.A1I5 Thermophilic composting of a synthetic JP-4 fuel mixture. McMullen, P.T.; Regan, R.W. Sr
Chelsen, Mich. : Lewis Publishers; 1992. Proceedings of the Industrial Waste Conference (46): p. 113-118; 1992. Meeting held May 14-16, 1991, West Lafayette, Indiana. Includes references.

Language: English

Descriptors: Polluted soils; Soil pollution; Fuels; Hydrocarbons; Bioremediation; Composting; Thermophilic microorganisms; Microbial degradation

157 NAL Call. No.: QH442.A1G4 Transposon vectors for stable chromosomal integration of cloned genes in rhizosphere bacteria.
Kaniga, K.; Davison, J.
Amsterdam : Elsevier Science Publishers; 1991. Gene v. 100: p. 201-205; 1991. Includes references.

Language: English

Descriptors: Pseudomonas; Chromosomes; Vectors; Cloning

Abstract: A series of Tn5-based transposon-cloning vectors, in which many, unique restriction sites lie within the transposon, have been constructed. These transposon vectors can be delivered, by conjugation, using a delivery vehicle containing, a pBR322 replicon and the mobilization genes of plasmid RK2. In Pseudomonas sp., this delivery vehicle acts as a suicide plasmid, permitting transposition to the chromosome to be detected. To facilitate cloning into the transposon vector, the delivery vehicle has been simplified so that the useful cloning sites in the transposon are not duplicated. As a model system for the transposition of cloned genes, the xy/E (coding for catechol-2,3-dioxygenase) has been transposed to a variety of Pseudomonads. The transposon vectors should be useful when a stable single copy of a cloned gene is desired. They should be particularly advantageous for the genetic engineering of soil bacteria for environmental studies (agriculture or pollution control) where the stability of the engineered strains, in the absence of continuous antibiotic selection, may be important.

158 NAL Call. No.: TA166.T72 US environmental regulations and policies--their impact on the commercial development of bioremediation.
Day, S.M.
Cambridge : Elsevier Science Publishing Co; 1993 Aug. Trends in biotechnology v. 11 (8): p. 324-328; 1993 Aug. In the special issue: Bioremediation: technological and commercial issues in the biological detoxification of polluted sites. Includes references.

Language: English

Descriptors: U.S.A.; Cabt; Pollution control; Bioremediation; Industrial methods; Environmental protection; Legislation; Federal government; Public agencies

159 NAL Call. No.: QD415.A1J62 Use of a mathematical model for prediction of optimum feeding strategies for in situ bioremediation.
Shouche, M.; Petersen, J.N.; Skeen, R.S. Totowa, N.J. : Humana Press; 1993.
Applied biochemistry and biotechnology v. 39/40: p. 763-779; 1993. Paper presented at the Fourteenth Symposium on Biotechnology for Fuels and Chemicals held May 11-15, 1992, Gathinburg, Tennessee. Includes references.

Language: English

Descriptors: Washington; Cabt; Polluted soils; Soil pollution; Bioremediation; Carbon tetrachloride; Microbial degradation; Mathematical models; Nutrient availability; Nitrate; Acetic acid

160 NAL Call. No.: QK710.P62 Use of roots transformed by Agrobacterium rhizogenes in rhizosphere research: applications in studies of cadmium assimilation from sewage sludges. Tepfer, D.; Metzger, L.; Prost, R.
Dordrecht : Kluwer Academic Publishers; 1989 Sep. Plant molecular biology : an international journal on molecular biology, biochemistry and genetic engineering v. 13 (3): p. 295-302; 1989 Sep. Paper presented at the symposium entitled "Plant Genetic Engineering Applications for Agriculture, Horticulture and Industry," September 26-29, 1989, Lunteren, The Netherlands. Literature review. Includes references.

Language: English

Descriptors: Calystegia sepium; Plants; Agrobacterium rhizogenes; Genetic transformation; Roots; Organ culture; Rhizosphere; Models; Ion uptake; Cadmium; Sewage sludge; Soil amendments; Soil pollution; Literature reviews

Abstract: The use of roots transformed by Agrobacterium rhizogenes in models for the rhizosphere is discussed. A list of species for which transformed root cultures have been obtained is provided and the example of studies of cadmium assimilation from sewage sludges is given to illustrate how transformed root cultures can be used in physiological tests under non-sterile conditions.

161 NAL Call. No.: TA166.T72 Using microorganims for biomediation: the barriers to implementation. Broda, P.
New York, N.Y. : Elsevier Science Publishing Co; 1992 Sep. Trends in biotechnology v. 10 (9): p. 303-304; 1992 Sep. Includes references.

Language: English

Descriptors: Pollution; Pollutants; Microbial degradation; Microbial flora; Genetic factors; Plasmids; Enzyme activity; Gene transfer; Genetic engineering; Biotechnology

162 NAL Call. No.: TA166.T72 The worldwide bioremediation industry: prospects for profit. Caplan, J.A.
Cambridge : Elsevier Science Publishing Co; 1993 Aug. Trends in biotechnology v. 11 (8): p. 320-323; 1993 Aug. In the special issue: Bioremediation: technological and commercial issues in the biological detoxification of polluted sites. Includes references.

Language: English

Descriptors: Pollution control; Bioremediation; Technology; Economic evaluation

Adenuga, A.O. 32
Aelion, C.M. 153
Akin, C. 29
Alexander, M. 14, 81, 83
Allan, D.L. 126
American Chemical Society, Division of Industrial and Engineering Chemistry,
American Chemical Society, Meeting_1991 :_Atlanta, Ga.) 92 Amrhein, C. 102
Anderson, T.A. 27
Anderson, W.L. 3
Andreyeva, A.L. 108
Anu Appaiah, K.A. 150
Apalovic, R. 76
Aronstein, B.N. 81
Arthur, M. 16
Arthur, M.F. 50
Atlas, R.M. 104
Aust, S.D. 117
Ausubel, K. 56
Bajpai, R. 36
Banerji, S. 36
Banks, M.K. 34
Barnes, D.J. 40
Baveye, P. 83
Beck, M.J. 23
Bedient, Philip B.,_1948 100
Bernstein, E. 148
Berti, W.R. 145
Bewley, R.J.F. 25
Biosystems Technology Development Program, United States, Environmental
Protection Agency 30
Blackburn, J.W. 105
Blackburn, James W., 90
Blanchette, R.A. 52
Blazej, A. 96
Bollag, J.M. 110, 122, 143
Bont, J.A.M. de 21
Bookum, W.M. ten 97
Bouwer, E.J. 31, 103
Braddock, J.F. 121
Brandle, J.E. 94
Broda, P. 48, 161
Brodkorb, T.B. 87
Brokamp, A. 155
Brooks, M.H. 84
Brown, E.J. 121
Brush, T.S. 52
Bumpus, J.A. 95, 129
Cachaza, J.M. 141
Calabrese, Edward J., 64
Caldwell, W.M. 54
Canhos, V.P. 134
Cannon, J.N. 32
Caplan, J.A. 162
Caton, J.E. 54
Chakrabarty, Ananda M.,_1938- 42
Chang, C.W. 129
Chapalamadugu, S. 124
Charbeneau, R. J. 100
Chaudhry, G.R. 124
Chollar, S. 138
Clark, J.C. 121
COGNIS, Inc, King Communications Group Inc 38 Cole, J. 66
Coleman, R.D. 95
Comeau, Y. 147
Cork, D.J. 152
Costa, G.F. 21
Cowan, A.K. 68
Coyle, C.G. 6
Crawford, D.L. 8, 109, 112, 149
Crawford, R.L. 8, 109, 112, 136, 149
Criddle, C.S. 85
Crouse, G. 7
Cunningham, S.D. 145
Dalev, P.G. 93
Davis, L.C. 17
Davison, J. 157
Day, S.M. 1, 158
Dec, J. 122
DeFlaun, M.F. 77
Delgado, I.L. 80
DeWitt, J.G. 3
Dhawan, S. 127
Dickinson, N.M. 2
Diels, L. 63
Dobbins, D.C. 153
Dragt, A. J. 39
Droege, M.W. 15
Duran, N. 134
Dutton, G. 49
Dutton, J. 53
Dwyer, D.F. 75
Dybas, M.J. 85
Dzantor, E.K. 23
Eckenfelder, W.W. Jr 9
Engelder, C.L. 28
Ensley, B.D. 12
Erickson, L.E. 17, 127
Esposito, E. 134
European Environmental Research Organisation, Commission of the European
Communities 115
Fan, L.T. 127
Farrell, R.L. 52
Federation of European Microbiological Societies 142 Felsot, A.S. 23
Ferraz, A. 134
Field, J.A. 21
Filip, Zdenek, 41
Finkelstein, N.P. 113
Focht, D.D. 88
Fox, Robert 90
Frankenberger, W.T. Jr 37
Fry, John C. 120
Funk, S.B. 8, 112
Gadd, G.M. 123
Galaska, E.G. 22
Galli, Enrica 142
Ganapathy, E.V. 73
Gannon, J. 83
Gannon, J.T. 14
Gauger, W.K. 29
Gibson, D.T. 6
Gold, M.H. 71
Gordon, M.P. 99
Graves, D.A. 146
Greenbaum, E. 55
Greer, C.W. 147
Greer, L.E. 82
Griest, W.H. 54
Grossman, M.J. 121
Guthrie, E.A. 27
Hadar, Y. 52
Hafker, W.R. 105
Ham, J. van 39
Hamasaki, A. 51
Hamer, G. 24
Han, K.H. 99
Hanna, M.L. 15
Hargis, M. 53
Harris, W.J. 59
Harvey, R.W. 84
Hattori, J. 94
Havel, J. 70
Hayes, T.D. 29
Heitzer, A. 128
Henis, Y. 132
Henrysson, T. 111
Hickey, R.F. 69
Hickey, W.J. 88
Hinchee, R.E. 16, 50
Hinchee, Robert E. 130, 131
Hirayama, K. 51
Ho, C.H. 54
Hoeppel, R.E. 50
Hooyberghs, L. 63
Hopkins, G.D. 125
Huang, W. 17
Hubbard, R.K. 118
Ikuta, Y. 51
Ingvorsen, H. 19
Innocentini-Mei, L.H. 134
Ironside, K.S. 54
Iverson, S. 52
Jablonski, P. 53
Jackson, P.J. 3
Janssen, D.B. 98
Jenkins, K.B. 10
Jensen, L.B. 151
Johnson, J.H. Jr 32
Johnstone, D.L. 107
Jones, K.C. 35
Jong, E. de 21
Just, S.R. 60
Kaake, R.H. 8
Kaiser, J.P. 110
Kakar, S.N. 95
Kamely, Daphne 42
Kandel, A. 154
Kaneva, Z. 151
Kaniga, K. 157
Karanth, N.G.K. 150
Karns, J.S. 46, 47
Karube, I. 40
Katayama, A. 135
Ke, H.Y.D. 3
Kearney, P.C. 47, 74
Keller, C.K. 107
Kelley, R.L. 29
Kennedy, J.F. 141
Kennes, C. 98
Kilbane, J.J. 29
King, R. Barry 139
King, R.J. 20
Knapp, R.M. 106
Kochmanska-Rdest, J. 76
Kosik, M. 96
Kostecki, Paul T. 64
Kreps, S. 63
Krisa, K. 52
Krumme, M.L. 75
Kuiper, E. 97
Kuske, C.R. 3
Labbe, H. 94
Laha, S. 86
LaJoie, C.A. 77
Lang, C.A. 146
Lange, C. 53
Lange, C.C. 57
Leavitt, M.E. 146
Lee, E. 17, 34
Lee, H. 89
Lee, S.A. 101
Legge, R.L. 87
Leonowicz, A. 76
Lepp, N.W. 2
Levanon, D. 132
Lewicka-Krol, Z. 76
Lewis, S.N. 55
Lewis, S.T. 18, 101
Lewis, T.A. 136
Lin, J.E. 69
Lindstrom, J.E. 121
Linz, D.G. 29
Liu, S. 79
Loehr, Raymond C. 100
Long, Gilbert M. 139
Lovett, P. S. 43
Lowrance, R. 118
Luthy, R.G. 86
Maart, B.A. 68
MacDonald, J.A. 133
MacInnis, J.M. 55
Mahmood, S.K. 119
Makita, T. 51
Malarczyk, E. 76
Mandelbaum, R.T. 126
Matson, S.A. 28
Matsumura, F. 135
McCarthy, A.J. 4
McCarty, P.L. 111, 125
McGinnis, G. 58
McInerney, M.J. 106
McMullen, P.T. 156
Mergeay, M. 63
Metge, D.W. 84
Metzger, L. 160
Michelsen, D.L. 10
Miki, B.L. 94
Mingelgrin, U. 14, 132
Minz, D. 113
Mitsch, W.J. 78
Molin, S. 151
Moller, J. 19
Moncrief, R.M. 3
Mongkolsuk, S. 43
Morgan, P. 18, 101
Mulbry, W. 74
Mulbry, W.W. 47
Negoro, M. 51
Norris, R.D. 9
Novak, J.T. 10
Nybroe, O. 154
Nyer, E.K. 22
Nyer, Evan K. 140
Ogunseitan, O.A. 80
Okeke, B.C. 5
Olfenbuttel, Robert F. 130, 131
Olsen, R.H. 20
Olson, B.H. 13, 80
Omenn, Gilbert S. 42
Orser, C.S. 53, 57
Ow, D.W. 137
Page, A.L. 102
Pardieck, D.L. 103
Park, S. 15
Parker, D.R. 102
Parkin, G.F. 6
Paterson, A. 5
Petersen, J.N. 159
Pfaender, F. 153
Phillips, T.D. 68
Piver, W.T. 65
Ploeg, J. van der 98
Portier, R.J. 11
Pries, F. 98
Prince, R.C. 121
Prost, R. 160
Ramos, J.L. 151
Rao, P.R. 119
Rasmussen, O.F. 154
Rayson, G.D. 3
Reardon, K.F. 91
Reed, Donald Timothy,_1956- 92
Regan, R.W. Sr 156
Reineke, W. 70
Renganathan, V. 71
Retana, J. 102
Riser-Roberts, Eve 33
Rittmann, B.E. 133
Roberts, D.J. 8, 112
Rochelle, P.A. 13
Rodriguez, M.J.M. 141
Roig, M.G. 141
Ron, E.Z. 113
Ronen, Z. 143
Rose, P.D. 68
Rosenberg, E. 113
Rothenburger, S. 104
Rowswell, R.A. 68
Samson, R. 147
Sanchez, L.M. 141
Sayler, G.S. 128
Sayler, Gary S.,_1949- 90
Schat, H. 97
Scheilbenbogen, K. 89
Schmidt, F.R.J. 155
Schneider, B.J. 57
Schnoor, J.L. 17
Schwartz, S. 73
Searles, D.B. 88
Seidler, R.J. 20
Semprini, L. 125
Sharma, P.K. 106
Shaw, D.M. 150
Sheldon, John K. 139
Shelton, D.R. 82
Sheppard, A.N. 101
Shih, J.C.H. 144
Shimp, J.F. 17
Short, K.A. 20
Shouche, M. 159
Shuttleworth, K.L. 122
Silver, S. 142
Simeonova, L.S. 93
Sisk, W.E. 61
Skeen, R.S. 159
Skladany, G.J. 22
Slepenkyn, A.V. 108
Smith, J.E. 5
Smith, M.C. 118
Smith, R.L. 84
Society for General Microbiology. Symposium. 1992 : University of Cardiff) 120
Spadaro, J.T. 71
Spiker, J.K. 109
Spilda, I. 96
Springael, D. 63
Srivastava, V.J. 29
Stahl, J.D. 117
Starovoytov, I.I. 108
Staszczak, M. 76
Stevens, T.O. 149
Stevenson, R.E. 62
Stewart, A.J. 54
Stockwell, K.J. 60
Stomp, A.M. 99
Stone, A.T. 103
Stratton, G.W. 67
Strom, P.F. 77
Stroo, H.F. 44
Sublette, K.L. 73
Suflita, J.M. 79
Suzuki, S. 51
Takeuchi, T. 40
Tan, E. 54
Tan, Y. 83
Tasker, I. R. 92
Tatara, G.M. 85
Taylor, R.T. 15
Tchelet, R. 132
Tepfer, D. 160
Thompson-Eagle, E.T. 37
Timmis, K.N. 75
Tracy, J.C. 17
Trempy, J. 43
Trevors, J.T. 89
Tsai, Y.L. 80
Tucker, S.L. 68
Turner, A.P. 2
Tursman, J.F. 152
Tyndall, R.L. 54
United States, Congress, Office of Technology Assessment 26 Vandegrift, G. F._1945- 92
Vellidis, G. 118
Verachtert, H. 115
Vereniging Lucht (Netherlands) 39
Verstraete, W. 115
Vooijs, R. 97
Wackett, L.P. 126
Wagenet, R.J. 14
Wall, A.J. 67
Walton, B.T. 27
Wan, L. 32
Wang, H.Y. 69
Warmbrodt, R.D. 45
Watkinson, R.J. 18, 101
Watmough, S.A. 2
Watson-Craik, I.A. 5
Wendler, P.A. 52
White, C. 123
Wiggert, L. 45
Wijngaard, A. van den 98
Wilbert, S. 99
Williams, R.T. 61
Williams, S.T. 4
Wilson, J.T. 72
Wilson, S.C. 35
Witholt, Bernard 142
Wood, B.D. 107
Woodward, C.A. 55
Worne, Howard E. 116
Xun, L. 53, 57
Yeager, T.R. 121
Zahrt, T.C. 57
Zehnder, A.J.B. 31
Zhang, G. 91
Ziegenfuss, P.S. 61
Zimmerman, W. 52
Zylstra, G.J. 77
Zytner, R.G. 89
2,4,5-t 74
2,4-d 20, 63, 74, 82, 154
2,4-dichlorophenol 122
3,4-dichloroaniline 101
Acclimatization 2
Acer pseudoplatanus 2
Acetates 6
Acetic acid 85, 159
Actinomycetales 4
Adaptation 153
Adenosine phosphates 84
Adsorption 3, 14
Aerobes 125
Aerobic treatment 6, 110
Aerobiosis 10, 103
Aggregates 127
Agricultural biotechnology 43
Agricultural chemicals 65
Agricultural soils 20, 37
Agrobacterium rhizogenes 99, 160
Air pollution 2, 40, 55
Air quality management 39
Alachlor 23
Alaska 121
Alcaligenes 19, 63, 143, 154, 155
Aldrin 11
Algae 40, 55, 68
Ambrosia 148
Amino acid sequences 53, 57
Anaerobes 25, 111
Anaerobic conditions 8, 18, 110, 112, 143, 149 Anaerobic digesters 144
Anaerobic treatment 8
Animal fat 93
Animal proteins 93
Animal wastes 118
Antibacterial properties 151
Apocynum 148
Application to land 9, 23, 84
Aquatic environment 138, 154
Aquifers 65, 72, 75, 83, 84, 85, 103, 106, 125, 136 Arizona 56
Aromatic acids 20
Aromatic compounds 135
Aromatic hydrocarbons 18, 21, 29, 32, 35, 81 Arthrobacter 11
Aspergillus niger 11
Astragalus racemosus 102
Atrazine 23, 126
Avena sativa 76
Azines 112
Azo compounds 112
Bacillariophyta 51
Bacillus licheniformis 144
Bacillus thuringiensis 49
Bacteria 12, 13, 22, 84, 98, 113, 125
Bacterial counting 150
Bacterial proteins 151
Benzene 14, 18, 22
Benzoates (esters) 151
Benzopyrene 101
Beta-glucosidase 134
Beta-glucuronidase 94
Bibliographies 45
Binding 113, 122
Binding proteins 137
Bioavailability 82, 105
Biochemical oxygen demand 146
Biochemical pathways 74, 110, 124
Biochemistry 105
Biodegradation 9, 17, 18, 32, 36, 42, 48, 49, 60, 71, 81, 103, 109, 114,
127, 132, 153
Biological activity in soil 34, 105, 107, 110, 133 Biological competition 52, 154
Biological fixed-film systems 22
Biological oxygen demand 103
Biological production 15, 93
Biological treatment 11, 12, 22, 28, 29, 40, 44, 51, 55, 62, 72, 73,
141
Biomass 113
Bioreactors 6, 10, 22, 40, 55, 72, 104 Bioremediation 3, 5, 6, 8, 9, 10, 11, 12, 16, 17, 18, 19, 23, 24, 25, 27,
31, 33, 34, 35, 38, 39, 42, 43, 46, 53, 54, 58, 59, 61, 63, 64, 65, 66, 67, 70,
75, 77, 79, 85, 88, 89, 91, 92, 99, 100, 101, 102, 104, 105, 106, 107, 111,
112, 113, 114, 117, 118, 119, 122, 125, 126, 128, 129, 130, 131, 132, 133, 134,
135, 136, 139, 140, 145, 146, 150, 151, 156, 158, 159, 162 Biosynthesis 137
Biotechnology 1, 7, 13, 43, 44, 45, 46, 48, 52, 56, 62, 68, 78, 123, 141,
142, 161
Biphenyl 77, 108
Bjerkandera adusta 21
Bleaching 52
Blue stain 52
Boron 102
Cabt 8, 58, 68, 84, 102, 158, 159
Cadmium 2, 94, 113, 137, 160
California 37, 102
Calystegia sepium 160
Carbamate pesticides 74, 124
Carbofuran 47
Carbon 101
Carbon cycle 4
Carbon dioxide 40, 51, 55, 107
Carbon tetrachloride 85, 136, 159
Carboxy-lyases 137
Carrion 93
Catabolism 80, 154
Cations 132
Cell growth 15
Cell suspensions 2, 3, 91
Cell walls 3
Cellulolytic microorganisms 96
Cellulose 48
Cellulose digestion 96
Ceriodaphnia dubia 54
Chemical reactions 53, 57, 104, 136
Chemistry 128
Chlorinated hydrocarbons 14, 98, 125, 135, 150, 152 Chlorophyta 51
Chlorpyrifos 95
Chlorthal-dimethyl 155
Chromosomes 157
Chrysosporium 101
Cloning 57, 108, 157
Cobalt 136
Community ecology 153
Comparisons 60
Composting 4, 32, 54, 61, 156
Concentration 117
Contaminants 34, 35, 61, 79, 110, 146
Contamination 22, 37, 46, 110
Copper 2, 67, 85, 97
Coriolus versicolor 21, 76, 101
Correlation 107
Coumaphos 47
Crops 49
Crosses 97
Crossing 97
Culture collections 62
Culture media 150
Culture techniques 147
Cultures 6, 62
Cycling 4, 37
Datura fastuosa 3
Decay fungi 21, 101, 135
Decolorization 134
Decontamination 13, 36, 98
Denitrification 110, 136
Denitrifying microorganisms 66, 136
Derivatives 104, 110
Detoxification 128
Diesel fuels 64
Diffusion of information 1
Diffusion of research 1
Digestibility 144
Digestion 93
Dinoseb 8, 149
Dissolved oxygen 18, 91
Dna 84
Dna hybridization 154
Dosage effects 154
Downward movement 14
Drinking water 6, 65
Drug resistance 150
Dunaliella 68
Dyes 71
Ecology 79
Economic evaluation 59, 162
Ecosystems 78
Efficiency 128
Electrical conductivity 102
Endomycetales 137
Energy content 84
Engineering 152
Enrichment 110, 149
Enumeration 150
Environment 45
Environmental biotechnology 26, 30, 41, 90, 115, 120 Environmental degradation 78, 124
Environmental factors 153
Environmental protection 26, 158
Enzyme activity 53, 57, 74, 75, 103, 111, 134, 137, 155, 161 Enzymes 48, 69
Escherichia coli 12, 57, 106, 108, 151 Ethanol 28
Evolution 79
Exhaust gases 51, 55
Explants 2
Explosives 54, 61, 73, 109, 112
Exposure 65, 110
Extraction 60
Factory effluents 11
Factory fumes 40
Feather meal 144
Feathers 144
Federal government 158
Feed additives 144
Fermentation 11, 96
Fermentation products 96
Ferric ions 85, 136
Ferrous ions 10, 136
Festuca rubra 76
Flavobacterium 47, 53, 57, 67, 138
Flow 83
Flushing 60
Fonofos 95
Forest trees 99
Fractionation 93
Fuels 156
Fungi 44
Gas production 29, 55
Gene expression 48, 57, 80, 94, 108
Gene interaction 97
Gene transfer 77, 155, 161
Genes 74, 77, 124
Genetic engineering 4, 12, 20, 25, 45, 49, 59, 63, 74, 98, 99< /A>, 148, 151,
161
Genetic factors 161
Genetic regulation 74
Genetic resources 62
Genetic transformation 57, 63, 94, 99, 108, 160 Genetic variation 79
Genetics 124
Genotypes 102
Georgia 118
Glucose 6, 96
Glutathione transferase 53
Glycolipids 89
Government research 1
Gracilicutes 47
Grasses 102
Groundwater 9, 10, 28, 75, 85, 153
Groundwater pollution 6, 10, 11, 13, 14, 17, 18, 22, 28, 31, 58, 65, 72, 75,
84, 85, 103, 111, 125, 127, 133, 136, 152, 153 Growth 67, 106, 155
Growth rate 97
Halogenated hydrocarbons 72, 152
Hazardous substances 116
Hazardous wastes 30
Heat treatment 60
Heavy metals 63, 102, 113, 123, 148
Herbicide residues 8, 20, 23
Herbicides 129
Heterogeneity 97
Humic acids 122
Humification 122
Hybrids 70
Hydrocarbons 16, 89, 121, 130, 131, 156 Hydrogen peroxide 5, 103
Hydrolases 155
Hydrolysis 132
Idaho 8
Immobilization 104
Immunoassay 7
Immunoblotting 154
Immunofluorescence 154
Indiana 110
Induction 80
Industrial methods 158
Industrial microbiology 52, 143
Industrial sites 29
Industrial wastes 24, 44, 141
Infiltration 14
Injuries 2
Inoculum 59, 77, 151
Inoculum density 19
Inonotus 76
Inorganic compounds 18
Insecticide residues 11
International cooperation 62
Introduced species 14, 20, 59, 150, 151 Ion uptake 160
Iron hydroxides 136
Isolation techniques 149, 150
Kinetics 69, 82
Kraft mill effluent 134
Laccase 134
Lakes 154
Leather waste 93
Leaves 94
Legislation 158
Lentinula edodes 5
Ligases 137
Lignin 48, 117, 129
Ligninolytic microorganisms 4, 21, 69, 117 Lignocellulose 4, 48, 96
Lignocellulosic wastes 4, 96
Literature reviews 4, 17, 35, 40, 74, 144, 152, 153, 160 Loam soils 14
Losses from soil systems 37
Lyases 53
Lycopersicon esculentum 49
Macropore flow 14
Major genes 97
Malathion 11
Marshes 56
Massachusetts 84
Mathematical models 106, 159
Measurement 107
Medicago sativa 34
Mercury 13
Metabolic detoxification 12, 74, 76, 99, 117, 145 Metabolism 77, 103, 111, 124, 125, 126 Metabolites 70, 125, 126, 129
Metal ions 3, 85, 132, 136
Metal tolerance 63, 97, 99, 102, 137
Metallothionein 94
Methane 15
Methanobacterium 15
Metolachlor 23
Microbial activities 18, 107, 122, 123 Microbial biotechnology 43, 116
Microbial degradation 4, 6, 8, 10, 11, 12, 14, 17, 19, 20, 21, 22, 23, 25,
27, 29, 31, 34, 44, 46, 47, 50, 52, 53, 57, 59, 62, 63, 67, 69, 70, 72, 73, 74,
75, 76, 77, 79, 80, 82, 85, 86, 87, 88, 91, 95, 96, 98, 101, 104, 110, 111,
112, 117, 119, 121, 124, 125, 126, 129, 134, 135, 136, 149, 150, 151, 152, 153,
154, 155, 156, 159, 161
Microbial flora 161
Microbial pesticides 59
Microorganisms 25, 34, 36, 59, 62, 74, 79, 133 Military areas 54
Mineralization 71, 86, 87, 88, 101, 112, 117, 121, 122, 124, 143, 149
Models 69, 160
Modifiers 97
Moisture content 19
Molasses 11
Molecular biology 12, 128
Molecular genetics 12
Monitoring 128, 150
Monophenol monooxygenase 134
Mortality 54
Motility 106
Movement 106
Movement in soil 14
Mushroom compost 5
Mutagenicity 54
Mutants 137
Mycelium 5, 117
Naphthalene 80, 111
Nature conservation 78
Netherlands 18
Nicotiana tabacum 94
Nitrate 85, 110, 159
Nitrogen 66, 117
Nitrogen fixing bacteria 66
Nitrogen-phosphorus fertilizers 121
Nocardia 76
Nonionic surfactants 77, 86
Nucleotide sequences 53, 57
Nutrient availability 8, 85, 159
Nutrient deficiencies 117
Nutrient sources 101
Nutrient uptake 37
O-glycoside hydrolases 134
Odor control 39
Oil pollution of soils 33, 64
Oil pollution of the sea 26
Oil pollution of water 33
Oil spills 26, 121
Ophiostoma 52
Optimization 15
Organ culture 160
Organic compounds 12, 27, 31, 103, 127, 146, 153 Organic matter 18
Organic nitrogen compounds 112, 129
Organochlorine compounds 53, 88
Organophosphate insecticides 74
Organophosphorus pesticides 124
Oryzopsis hymenoides 102
Oxidation 68, 103, 111, 129
Oxygen 10, 55, 110
Oxygenases 15, 57, 75, 108, 111
Parathion 132
Pentachlorophenol 5, 36, 53, 57, 67, 69, 74 Peptides 137
Peroxidases 103, 117, 129, 134
Persistence 110, 149
Pest resistance 49
Pesticide residues 36, 74, 124
Pesticides 44, 46, 49, 138
Petroleum 16, 22, 33, 34
Petroleum hydrocarbons 22, 28, 50
Ph 85, 113
Phanerochaete chrysosporium 21, 25, 48, 69, 71, 73, 87, 95, 101, 109, 117,
129, 135
Phenanthrene 19, 86, 87, 119
Phenol 6, 76, 125
Phenolic acids 80
Photolysis 36, 135
Photosynthesis 40, 51, 55
Phthalates 91
Physiology 79
Phytotoxicity 2, 76
Pitch 52
Plants 17, 145, 160
Plasmid vectors 77, 108, 151
Plasmids 63, 108, 154, 155, 161
Pleurotus ostreatus 76
Pollutants 14, 17, 21, 25, 31, 32, 34, 59, 65, 66, 87, 99, 103, 109, 122,
123, 135, 145, 152, 161
Polluted soils 7, 8, 17, 20, 22, 23, 25, 29, 34, 35, 54, 59, 76, 77, 89, 99,
101, 110, 112, 126, 132, 145, 150, 151, 152, 153, 156, 159 Polluted water 7, 17, 154
Pollution 78, 141, 161
Pollution control 24, 31, 66, 105, 118, 123, 128, 158, 162 Polychlorinated biphenyls 63, 70, 77, 88 Polycyclic hydrocarbons 21, 29, 32, 119 Polyhydroxybutyrate 111
Polymerization 122
Polyporus 21
Ponds 68
Population density 34
Population dynamics 80
Populations 97
Pore size 14, 106
Pores 106
Poultry manure 144
Power industry 51
Preservation 62
Product development 49
Production economics 59
Proteinases 93, 144
Pseudomonas 11, 77, 80, 83, 85, 132, 136, 142, 150, 157 Pseudomonas aeruginosa 88, 89, 108
Pseudomonas cepacia 70, 75, 147
Pseudomonas fluorescens 25, 155
Pseudomonas putida 6, 10, 20, 25, 88, 104, 108, 151 Public agencies 158
Pulp mill effluent 134
Purines 137
Pycnoporus sanguineus 134
Pyridines 110, 143
Quinoline 104
Quinolines 104
Radionuclides 123
Reclamation 29, 37, 118
Recombinant DNA 4, 12, 77, 94, 151, 154 Recombination 20
Redox potential 110
Reduction 110, 117
Regulation 136
Reporter genes 94
Research 1
Resins 52
Respiration 107
Respiratory gases 146
Reviews 103, 141
Rhizosphere 17, 27, 34, 160
Riparian forests 118
Roots 94, 97, 160
Rotating biological contactors 28, 73
Runoff 118
Salicylates 80
Salinity 68
Salt tolerance 102
Sand 83, 106
Sandy loam soils 89
Sandy soils 106
Saskatchewan 107
Saturated conditions 14, 83
Sawdust 76
Seasonal fluctuations 107
Sediment 21
Segregation 97
Selenium 37
Separation (Technology) 92
Sewage effluent 84
Sewage effluent disposal 84
Sewage sludge 160
Shoots 2, 102
Silene vulgaris 97
Silt loam soils 86
Simulation models 127
Sodium chloride 83
Soil 10, 81, 127
Soil air 22
Soil amendments 76, 101, 160
Soil bacteria 4, 14, 29, 70, 82, 88, 91, 108, 119, 126, 14 7, 149, 155
Soil depth 102, 107
Soil flora 17, 23, 37, 80, 86, 91, 110, 122, 152, 153 Soil fungi 119
Soil inoculation 19, 25, 88, 147
Soil mechanics 14
Soil organic matter 82
Soil ph 112
Soil pollution 5, 8, 9, 14, 16, 17, 19, 20, 21, 22, 23, 25, 27, 29, 31, 32,
36, 37, 41, 50, 53, 58, 60, 61, 70, 76, 82, 87, 89, 92, 99, 100, 101, 103, 105,
108, 109, 112, 113, 119, 122, 127, 129, 133, 140, 145, 146, 149, 150, 152, 153,
155, 156, 159, 160
Soil temperature 107
Soil treatment 105
Solubilization 86
Solvents 60
South Africa 68
South Carolina 110
Spatial distribution 14
Starch 8
Strains 14, 21, 82, 113, 135
Streptomyces 48
Streptomycin 150
Stress response 2
Structural genes 53, 57, 80, 94, 151
Substrates 6, 82, 101, 155
Subsurface layers 107, 152, 153
Sucrose 11
Sugar factory waste 11
Sulfate 110
Surface layers 110
Surfactants 81, 89
Survival 154, 155
Sustainability 62
Tannery waste 68
Tars 87
Technical progress 1
Techniques 105, 128
Technology 60, 162
Technology transfer 1, 62
Temperature 18, 91
Terbufos 95
Thermophilic microorganisms 156
Toluene 14, 18, 22, 109, 117, 125
Tonoplast 137
Town gas 29
Toxic substances 128, 135
Toxicity 67, 117
Transformation 37, 110, 149
Transgenic plants 94
Transport processes 65, 83
Transposable elements 151
Treatment 58, 123
Tree breeding 99
Trees 99
Triazine herbicides 74
Trichloroethylene 6, 75, 111, 125
Trifluralin 23
U.S.A. 58, 158
Uk 2
Ultrafiltration 68
Ultraviolet radiation 135
Uptake 94, 99, 102, 137, 145
Vacuoles 137
Vectors 157
Velocity 83
Volatile compounds 6
Washing 60
Washington 107, 159
Wastage 48
Waste disposal 60
Waste disposal sites 46
Waste treatment 1, 46, 74, 128, 138, 148 Waste utilization 48, 93
Waste water 73, 141
Waste water treatment 9, 11, 56, 68, 73 Wastes 12, 62
Water microbiology 153
Water pollution 113, 118, 149
Water purification 28
Water quality 118
Water resources 56
Water, Underground 41, 92, 100, 140
Wetlands 56, 118
Wood 58
Wood chips 52
Wood dust 76
Wood pulp 52
Xanthomonas 132
Xenobiotics 130, 131
Xylene 10, 18, 22
Xylose 96
Yeast extracts 69
Yields 102