Academic literature on the topic 'Earthworms – Effect of chemicals on'
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Journal articles on the topic "Earthworms – Effect of chemicals on"
Hur, Jaeryung, and Eun Hea Jho. "Current Research Trends on the Effects of Microplastics in Soil Environment Using Earthworms: Mini-Review." Journal of Korean Society of Environmental Engineers 43, no. 4 (2021): 299–306. http://dx.doi.org/10.4491/ksee.2021.43.4.299.
Full textMiglani, Rashi, and Satpal Singh Bisht. "World of earthworms with pesticides and insecticides." Interdisciplinary Toxicology 12, no. 2 (2019): 71–82. http://dx.doi.org/10.2478/intox-2019-0008.
Full textŠestinová, Oľga, Lenka Findoráková, Silvia Dolinská, Jozef Hančuľák, Tomislav Špaldon, and Erika Fedorová. "Effect Of Environmental Load On The Toxicity Of Bottom Sediments." Nova Biotechnologica et Chimica 14, no. 1 (2015): 78–86. http://dx.doi.org/10.1515/nbec-2015-0017.
Full textEhouman, N’guetta Moïse, Mamadou Touré, Pkan Pkan Kouakou Gains, Hervé Kouya Bi, and Seydou Tiho. "Effect of Different Agroecosystem on Earthworm Diversity in Azaguié Locality (Côte d'Ivoire)." Journal of Biology and Life Science 11, no. 2 (2020): 327. http://dx.doi.org/10.5296/jbls.v12i1.17936.
Full textLONG, WONECA, ABDULLAH ANSARI, and DIANA SEECHARRAN. "The effect of urea on epigeic earthworm species (Eisenia foetida)." Cell Biology and Development 1, no. 2 (2017): 46–50. http://dx.doi.org/10.13057/cellbioldev/v010202.
Full textWu, Zexuan, Bangyi Yin, Xu Song, and Qi Zhao. "Effects of different lipid contents on growth of earthworms and the products during vermicomposting." Waste Management & Research 37, no. 9 (2019): 934–40. http://dx.doi.org/10.1177/0734242x19861683.
Full textKaka, H., P. A. Opute, and M. S. Maboeta. "Potential Impacts of Climate Change on the Toxicity of Pesticides towards Earthworms." Journal of Toxicology 2021 (August 20, 2021): 1–14. http://dx.doi.org/10.1155/2021/8527991.
Full textGobi, Muthukaruppan, and Paramasamy Gunasekaran. "Effect of Butachlor Herbicide on EarthwormEisenia fetida—Its Histological Perspicuity." Applied and Environmental Soil Science 2010 (2010): 1–4. http://dx.doi.org/10.1155/2010/850758.
Full textMuchane, Mary N., Mirjam M. Pulleman, Bernard Vanlauwe, Joyce Jefwa, and Thomas W. Kuyper. "Impact of arbuscular mycorrhizal fungi and earthworms on soil aggregate stability, glomalin, and performance of pigeonpea, Cajanus cajan." Soil Research 57, no. 1 (2019): 53. http://dx.doi.org/10.1071/sr18096.
Full textVáclav, Pižl, Jiří Schlaghamerský, and Jan Tříska. "The effects of polycyclic aromatic hydrocarbons and heavy metals on terrestrial annelids in urban soils." Pesquisa Agropecuária Brasileira 44, no. 8 (2009): 1050–55. http://dx.doi.org/10.1590/s0100-204x2009000800038.
Full textDissertations / Theses on the topic "Earthworms – Effect of chemicals on"
Goats, Geoffrey Charles. "Assessment of the effects of toxic chemicals upon earthworms." Thesis, Imperial College London, 1985. http://hdl.handle.net/10044/1/37706.
Full textGola, Nontuthuzelo Pearl. "A comparison of biomarkers in assessing the combined effects of pesticide mixtures on non-target soil invertebrates." Thesis, Stellenbosch : University of Stellenbosch, 2004. http://hdl.handle.net/10019.1/16327.
Full textENGLISH ABSTRACT: Agricultural environments are usually contaminated with mixtures of antropogenically introduced chemicals as a result of pesticide spraying, which can affect beneficial, nontarget soil invertebrates, such as earthworms negatively. Most studies on mixture toxicity have focused on interactions of chemicals with similar structures and mechanisms. However, chemical mixtures may occur as conglomerates of diverse structures and toxicological mechanisms in the environment. This study was aimed at assessing the effects of pesticides singly, and in a mixture, on earthworms, using lifecycle parameters (growth and reproduction) and biomarkers (neutral red retention (NRR) assay and acetylcholinesterase (AChE) inhibition) as endpoints. Thus, to determine whether any interactions occurred between the pesticides as shown by the measured endpoints. Another aim was to validate the use of the chosen biomarkers for assessing mixture toxicity. The pesticides used were from three groups: organophosphates, heavy metal-containing pesticides and pyrethroids. From these three groups, four of the most commonly used pesticides in the orchards and vineyards of the Western Cape, South Africa, were chosen, namely chlorpyrifos (organophosphate), azinphos-methyl (organophosphate), copper oxychloride (heavy metal-containing fungicide) and cypermethrin (pyrethroid). Earthworms were exposed in the laboratory to a range of concentrations of chlorpyrifos and copper oxychloride singly, and in 1:1 mixtures of these pesticides in artificial soil, for four weeks. After the exposure period, the biomass change was determined as measure of growth, and cocoon production, hatching success and number of hatchlings per cocoon were determined as measures of reproduction. Growth (biomass change) and reproduction (cocoon production) were affected by the highest concentration treatment (20mg/kg) of chlorpyrifos, but copper oxychloride and the mixture of the two pesticides showed no observable effects on lifecycle parameters. Dose related effects on NRR times were however determined for both pesticides and the mixture. Dose related effects on AChE activity were found for chlopyrifos and the mixture of the two pesticides, but not for copper oxychloride. Short-term exposures (48 hours) of earthworms to the following pesticides in artificial groundwater: chlorpyrifos, copper oxychloride, azinphos-methyl, cypermethrin, chlorpyrifos-copper oxychloride, chlorpyrifos -azinphos-methyl and chlorpyrifos-cypermethrin, were done followed by the determination of AChE inhibition. Dose related effects were exhibited on the AChE activity of earthworms exposed to chlorpyrifos, a mixture of chlorpyrifos and copper oxychloride, azinphos-methyl, and a mixture of azinphos-methyl and chlorpyrifos. Copper oxychloride, cypermethrin and the mixture of chlorpyrifos and cypermethrin had no effect on AChE activity. Earthworms died at the highest exposure concentration of the mixture of chlopyrifos and cypermethrin. Results have shown that although the pesticides did not cause observable effects on lifecycle parameters, there were effects at subcellular and biochemical level, as shown by the biomarkers. Mixtures of pesticides, in some instances, affected earthworms differently from their single components, indicating interactions between the pesticides in mixtures, as shown by the measured endpoints. The NRR assay proved to be a good general biomarker of soil contamination, and the AChE activity could also be a valuable tool in assessing the effects of organophosphate mixtures and mixtures of organophosphates and pesticides from other groups.
AFRIKAANSE OPSOMMING: Nie-teiken organismes, soos erdwurms, word negatief beïnvloed deur mengsels van antropogeniese chemikalieë in landbou-omgewings. Die meeste studies wat handel oor die toksisiteit van chemiese mengsels het tot dusver gefokus op chemikalieë van dieselfde aard en met dieselfde meganismes van werking. Mengsels van chemiese stowwe kan egter as konglomerate van 'n verskeidenheid strukturele eienskappe en met verskillende toksiese meganismes in die omgewing aangetref word. Tydens die studie is gepoog om die effekte van enkel pestisiede sowel as mengsels daarvan op erdwurms te bestudeer, deur van lewensloop kenmerke (groei en voortplanting) en biomerkers (neutraalrooi retensietyd - NNR en inhibisie van asetielcholienesterase -AChE) as eindpunte gebruik te maak. 'n Verdere doel van die studie was om vas te stel of daar enige wisselwerkings tussen die verskillende pestisiede plaasvind, soos aangetoon deur die gemete eindpunte, en verder ook om die gebruik van die gekose biomerkers as maatstawwe van mengseltoksisiteit te evalueer. Die pestisiede wat gebruik is, is van drie verskillende groepe afkomstig: organofosfate, swaarmetale en piretroiede. Van hierdie drie groepe is vier van die pestisiede wat vry algemeen in boorde en wingerde in die Weskaap, Suid-Afrika, gebruik word, geïdentifiseer. Hierdie stowwe is chlorpyrifos (organofosfaat), azinphos-metiel (organofosfaat), koperoksichloried (swaarmetaalbevattende fungisied) en sipermetrien (piretroied). Erdwurms is in die laboratorium aan 'n reeks konsentrasies van chlorpyrifos en koperoksichloried as enkel toksikante en as 1:1 mengsels in kunsmatige grond, vir vier weke blootgestel. Voor en na die blootstellingsperiode is die biomassa van die wurms, as maatstaf van groei, bepaal en kokonproduksie, uitbroeisukses en getal nakomelinge per kokon bepaal as maatstawwe van voortplantingsvaardigheid. Groei (biomassaverandering) en voortplanting (kokonproduksie) is beinvloed deur behandeling met die hoogste konsentrasie (20 mg/kg) chlorpyrifos, terwyl geen effek van koperoksichloried of die mengsel van hierdie twee pestisiede gevind is nie. Daar is gevind dat beide die pestisiede, enkel en in die mengsel, die NRR tye beinvloed het. Die AChE aktiwiteit is beinvloed deur chlorpyrifos en die mengsel, maar nie deur die koperoksichloried nie. Korttermyn blootstellings van erdwurms (48 uur), in kunsmatige grondwater, van erdwurms aan chlorpyrifos, koperoksichloried, azinphos-metiel en sipermetrien as enkel toksikante en mengsels van chlorpyrifos-koperoksichloried, chlorpyrifos-azinphos-metiel en chlorpyrifos-sipermetrien, is gedoen en gevolg deur die bepaling van AChE inhibisie. Koperoksichloried, cypermetrien en die chlorpyrifos-sipermetrien mengsel het geen waarneembare effek op die AChE aktiwiteit gehad nie ?????. Die erdwurms wat blootgestel is aan die hoogste konsentrasie in die mengsel van chlorpyrifos-sipermetrien het doodgegaan. Die resultate het getoon dat die pestisiede nie in die korttermyn die lewensloopkenmerke in enige waarneembare mate geaffekteer het nie maar daar was effekte op sellulêre en biochemiese vlakke soos aangetoon deur die biomerkers. Sommige mengsels van die pestisiede het die erdwurms verskillend van die enkelstowwe geaffekteer. Daar het dus wisselwerking tussen sommige van die pestisiede wat in mengsels aangewend is, plaasgevind, soos aangetoon deur die gemete eindpunte. Die NRR toets, as breë-spektrum biomerker was 'n goeie maatstaf van kontaminasie in grond en daar is aanduidings dat die AChE aktiwiteit, as 'n spesifieke biomerker, 'n nuttige maatstaf kan wees om die effekte van organofosfaatmengsels en mengsels van hierdie chemiese groep en die van ander chemikalieë aan te toon.
Wong, Stephen W. "Reproductive toxicity and bioavailability of arsenic in contaminated artificial and natural soils using the earthworm." Thesis, McGill University, 2003. http://digitool.Library.McGill.CA:80/R/?func=dbin-jump-full&object_id=79205.
Full textLeduc, Frédéric. "Linking the neuropeptide annetocin with reproductive success of the earthworm Eisenia fetida in two natural soils amended with the wood preservatives chromated copper arsenate (CCA) and alkaline copper quaternary (ACQ)." Thesis, McGill University, 2004. http://digitool.Library.McGill.CA:80/R/?func=dbin-jump-full&object_id=82274.
Full textVoua, otomo Patricks. "The effects of long-term exposure to cadmium on the earthworm Eisenia Fetida (Oligochaeta) : an investigation of the development of genetic metal resistance." Thesis, Stellenbosch : Stellenbosch University, 2006. http://hdl.handle.net/10019.1/22010.
Full textENGLISH ABSTRACT: The development of potential genetically based resistance to cadmium (Cd) after long-term exposure to this metal at a sublethal concentration, was investigated in earthworm specimens belonging to the genus Eisenia. Adult (clitellate) earthworms from a long-term laboratory Cdexposed population (> 78 generations) and from other populations having no previous history of metal exposure were exposed to increasing concentrations (0; 2.5; 5; 10 and 20 mg/l) of Cd in the form of CdSO4. Different biomarkers and molecular markers were used to determine whether the specimens from the long-term Cd-exposed population had acclimatized or adapted to the metal contaminated environment. Acclimation was investigated at different physiological and biochemical levels using the following three biomarkers: the 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyl tetrazolium bromide assay (MTT assay) measuring mitochondrial activity and cell viability; the single cell gel electrophoresis assay (comet assay) measuring DNA strand breaks and the biosynthesis of metallothioneins (MTs) that have the function of lowering metal toxicity. Earthworms from the long-term exposed substrate as well as specimens from populations not exposed to Cd were used. Adaptation was investigated by looking at both allozyme polymorphism at seven enzyme encoding loci and DNA polymorphism using chosen neutral and selectable genetic markers. The markers used were cytochrome c oxydase subunit I (COI) and metallothionein-2 (mt-2) respectively. This was done amongst the same pool of populations. Additionally, the DNA polymorphism study also aimed at genetically identifying the species utilized in this study thereby determining whether these earthworms belong to the species Eisenia fetida or Eisenia andrei. MTs biosynthesis did not generate the expected data mainly due to the fact that a suitable antibody could not be obtained (discussed in Chapter 5 section 5.3.3.). Similarly, the assessment of DNA polymorphism at the chosen selectable genetic marker mt-2 did provide information relevant to understanding the potential development of resistance to Cd in the long-term metal contaminated group. COI sequences generated in this study were compared to E. fetida and E. andrei COI sequences available on Genbank. Consequently, specimens used in this study were identified as possibly belonging to the species E. andrei. Allozyme polymorphism revealed no fixed genetic differences between the long-term Cd exposed laboratory culture and the rest of the populations. All the populations departed from Hardy-Weinberg equilibrium (χ2 > 5.9; p < 0.05), and showed a low mean heterozygosity per locus (Ho ≤ 0.21), probably due to inbreeding. Cell viability and proliferation as tested by the MTT assay revealed that coelomocytes, isolated from the long-term Cd-exposed group showed the highest viability (98.42%) compared to those from other groups (+/- 80%). Kruskal-Wallis ANOVA (H2, 225=109.7165 p < 0.001) revealed that the long-term Cd-exposed laboratory culture showed a better response to acute exposure to Cd, thus demonstrating that these worms have developed some kind of tolerance to Cd. Similarly, the comet assay showed that in the long-term Cd-exposed specimens, less DNA breaks occurred after Cd exposure than in the unexposed groups. Of all the comet parameters assessed in this study (comet tail length, tail moment and tail DNA percentage), tail DNA percentage seemed to be more sensitive although all three parameters indicated that long-term Cd-exposed specimens were more resistant than unexposed specimens as shown by the number of single strand DNA breaks induced by exposure to higher concentrations of Cd (p < 0.001). The comet and the MTT assays indicated that the earthworms with a previous history of Cd exposure have developed increased fitness towards higher doses of Cd, compared to previously unexposed groups. These findings mainly proved that several mechanisms could come into play at the physiological and biochemical level to allow the Cd exposed population to acclimatize to its chemically stressful environment. Clear genetic support for the differences found between the tested populations was not obtained, but needs to be investigated further using Cd selectable markers such as the mt-2 gene, in order to come to a more conclusive deduction.
AFRIKAANSE OPSOMMING: Die moontlike ontwikkeling van geneties gebaseerde weerstand teen kadmium (Cd) by erdwurms van die genus Eisenia, na langtermyn blootstelling aan die metaal by 'n subletale konsentrasie, is ondersoek. Volwasse (klitellate) erdwurms van 'n langtermyn laboratorium Cdblootgestelde bevolking (< 78 generasies) asook van ander bevolkings met geen voorgeskiedenis van metaal blootstelling nie, is blootgestel aan 'n reeks van Cd konsentrasies (0; 2.5; 5; 10; en 20 mg/l) in die vorm van CdSO4. Verskillende biomerkers en molekulêre merkers is gebruik om vas te stel of die erdwurms geakklimeer of aangepas het by die metaal in die gekontamineerde omgewing. Akklimasie is op verskillende fisiologiese en biochemiese vlakke getoets deur die volgende drie biomerkers te gebruik: Die 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyl tetrazolium bromied toets (MTT toets), wat mitochondriale aktiwiteit en sel lewensvatbaarheid meet; die enkel sel elektroforese toets (Komeettoets) wat DNS string breuke meet; die biosintese van metallotioniene (MT's) wat metaalvergiftiging verlaag. Erdwurms van die langtermyn blootstellingsubstraat asook eksemplare van bevolkings wat nie aan kadmium blootgestel was nie, is gebruik. Aanpassing is ondersoek deur gebruik te maak van allosiem polimorfisme, waar 7 ensiem koderende lokusse gebruik is asook van DNS polimorfisme deur neutrale genetiese merkers te selekteer. Die merkers wat gebruik is, was sitochroom c oksidase, subeenheid I (COI) en metallotionien-2 (mt-2) respektiwelik. Hierdie toetse is met dieselfde groepe bevolkings uitgevoer. 'n Bykomende van die studie aspek waar ook van DNS polimorfisme gebruik gemaak is, was daarop gemik om die spesie wat vir die huidige studie gebruik is, geneties te identifiseer en om vas te stel of die erdwurms aan die spesie Eisenia fetida of Eisenia andrei behoort. Die MT biosintese het nie die verwagte data gegenereer nie, hoofsaaklik weens die feit dat geskikte teenligaampies nie beskikbaar was nie (bespreek in Hoofstuk 5 afdeling 5.3.3). Soortgelyk, het die waardebepaling van DNS polimorfisme by die geselekteerde genetiese merker mt-2 nie genoegsame informasie verskaf om die potensiaal van die ontwikkeling van weerstand teen Cd in die langtermyn blootgestelde groep te verstaan nie. COI geenvolgordes van E. fetida en E. andrei wat op Genbank beskikbaar was, is gebruik om met die resultate van die huidige studie te vergelyk. Die spesie wat tydens die huidige studie gebruik is, is op hierdie wyse geïdentifiseer as E. andrei. Allosiem polimorfisme het geen vaste genetiese verskille tussen die langtermyn blootgestelde laboratoriumkulture en die ander bevolkings getoon nie. Al die bevolkings het verskil van die Hardy-Weinberg ewewigstoestand (χ2 > 5.9; p < 0.05) en het 'n lae heterosigositeit per lokus getoon (Ho ≤ 0.21), moontlik as gevolg van inteling. Sellewensvatbaarheid en proliferasie soos getoets met die MTT toets, het getoon dat selomosiete, geïsoleer vanuit die langtermyn Cd blootgestelde groep, die hoogste lewensvatbaarheid (98.42%) gehad het in vergelyking met die ander groepe (+/- 80%). Kruksal-Wallis ANOVA (H2, 225=109.7165 p < 0.001) het getoon dat die langtermyn Cd blootgestelde laboratoriumkultuur 'n beter respons vir akute blootstelling aan Cd gehad het. Hierdeur is gedemonstreer dat hierdie wurms 'n soort toleransie teenoor kadmium ontwikkel het. Soortgelyk het die komeettoets aangetoon dat daar in die langtermyn blootgestelde eksemplare minder DNS breuke voorgekom het na verdere blootstelling aan Cd as in die ander groepe. Van al die komeet parameters wat tydens die studie gemeet is (komeet stertlengte, Olive stert moment en stert DNS persentasie), het die stert DNS persentasie geblyk om die mees sensitiefste te wees, alhoewel al drie parameters aangetoon het dat die langtermyn Cd blootgestelde eksemplare meer weerstandbiedend was teen induksie van DNS enkelstring breuke weens Cd blootstelling (p < 0.001), as die wat nie voorheen blootgestel was nie. Die komeet en MTT toetse het aangetoon dat erdwurms met 'n voorgeskiedenis van Cd blootstelling 'n toenemende fiksheid teen hoër dososse van Cd ontwikkel het as die wat nie voorheen aan kadmium blootgestel was nie. My bevindings kon hoofsaaklik toon dat verskeie meganismes op die fisiologiese en biochemiese vlak 'n rol sou kon speel om Cd blootgestelde bevolkings by 'n chemies stresvolle omgewing te laat akklimeer. Duidelike ondersteuning vir die verskille tussen die getoetsde bevolkings deur van Cd geselekteerde merkers soos die mt-2 geen gebruik te maak om 'n meer finale afleiding te kan maak is nie verkry nie en behoort verder ondersoek te word.
Filby, Amy Louisa. "Molecular effect pathways of endocrine disrupting chemicals in fish." Thesis, University of Exeter, 2006. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.439828.
Full textEyambe, George Sona. "Cellular Biomarkers for Measuring Toxicity of Xenobiotics: Effects of PCBs on Earthworm Lumbricus Terrestris Coelomocytes." Thesis, University of North Texas, 1991. https://digital.library.unt.edu/ark:/67531/metadc332716/.
Full textCoberly, Samantha W. "The effect of household chemicals on deciduous and permanent tooth class." Thesis, Wichita State University, 2013. http://hdl.handle.net/10057/6807.
Full textThesis (M.A.)--Wichita State University, Fairmount College of Liberal Arts and Sciences, Dept. of Anthropology
Turan, Nahid. "The effect of plasticisers and related chemicals on sulphate supply enzymes." Thesis, University of Birmingham, 2006. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.433746.
Full textDelacruz, C. Ligia. "The effect of natural toxicants and other chemicals on the kidney." Thesis, University of Surrey, 1988. http://epubs.surrey.ac.uk/847359/.
Full textBooks on the topic "Earthworms – Effect of chemicals on"
1951-, Sheppard Stephen, and SETAC (Society), eds. Advances in earthworm ecotoxicology: Proceedings from the Second International Workshop on Earthworm Ecotoxicology, April 1997, Amsterdam, the Netherlands. SETAC Press, 1998.
Riepert, Frank. Development of laboratory methods for testing effects of chemicals and pesticides on Collembola and earthworms =: Entwicklung von Labormethoden zur Prüfung der Wirkung von chemischen Stoffen und Pflanzenschutzmitteln auf Collembolen und Regenwürmer. Parey, 1996.
Płytycz, Barbara. Earthworms for monitoring metal contamination. Nova Science, 2009.
Lee, Betty Lou. Coping with chemicals. Environment Canada, 1985.
Halton, David M. What makes chemicals poisonous? Canadian Centre for Occupational Health & Safety, 1988.
The poison paradox: Chemicals as friends and foes. Oxford University Press, 2005.
The poison paradox: Chemicals as friends and foes. Oxford University Press, 2008.
Japan. Kankyōshō. Kankyō Hokenbu. Kankyō Risuku Hyōkashitsu. Nihonjin ni okeru kagaku busshitsu no bakuroryō ni tsuite: Kagaku busshitsu no hito e no bakuroryō monitaringu chōsa (2011-) = The exposure to chemical compounds in the Japanese people. Kankyōshō Kankyō Hokenbu Kankyō Risuku Hyōkashitsu, 2014.
Nong zuo wu nong yao zhi yao hai. Dao xiang wen hua shi ye gu fen you xian gong si, 1994.
Kaiser, Klaus L. E. Ecotoxicity of chemicals to photobacterium phosphoreum. Gordon and Breach Science Publishers, 1994.
Book chapters on the topic "Earthworms – Effect of chemicals on"
Edwards, Clive A., and Patrick J. Bohlen. "The Effects of Toxic Chemicals on Earthworms." In Reviews of Environmental Contamination and Toxicology. Springer New York, 1992. http://dx.doi.org/10.1007/978-1-4612-2890-5_2.
Full textAndrews, D. F., and A. M. Herzberg. "Effect of Chemicals on Earthworm Populations." In Springer Series in Statistics. Springer New York, 1985. http://dx.doi.org/10.1007/978-1-4612-5098-2_53.
Full textVonk, J. W., D. M. M. Adema, and D. Barug. "Comparison of the Effects of Several Chemicals on Microorganisms, Higher Plants and Earthworms." In Contaminated Soil. Springer Netherlands, 1986. http://dx.doi.org/10.1007/978-94-009-5181-5_25.
Full textWeekers, F., Ph Thonart, Ph Jacques, D. Springael, M. Mergeay, and L. Diels. "Effect of Drying on Bioremediation Bacteria Properties." In Biotechnology for Fuels and Chemicals. Humana Press, 1998. http://dx.doi.org/10.1007/978-1-4612-1814-2_30.
Full textDu, Liping, Aleš Prokop, and Robert D. Tanner. "Effect of Bubble Size on Foam Fractionation of Ovalbumin." In Biotechnology for Fuels and Chemicals. Humana Press, 2002. http://dx.doi.org/10.1007/978-1-4612-0119-9_87.
Full textBredwell, M. D., M. D. Telgenhoff, S. Barnard, and R. M. Worden. "Effect of Surfactants on Carbon Monoxide Fermentations by Butyribacterium methylotrophicum." In Biotechnology for Fuels and Chemicals. Humana Press, 1997. http://dx.doi.org/10.1007/978-1-4612-2312-2_56.
Full textBurapatana, Vorakan, Ernest E. Butler, Gaurav Chauhan, et al. "Effect of Lidocaine on Ovalbumin and Egg Albumin Foam Stability." In Biotechnology for Fuels and Chemicals. Humana Press, 2003. http://dx.doi.org/10.1007/978-1-4612-0057-4_76.
Full textGottschalk, Leda M. F., Ronaldo Nobrega, and Elba P. S. Bon. "Effect of Aeration on Lignin Peroxidase Production by Streptomyces viridosporus T7A." In Biotechnology for Fuels and Chemicals. Humana Press, 2003. http://dx.doi.org/10.1007/978-1-4612-0057-4_67.
Full textSaxena, Ajit Kumar, and Amit Kumar. "Effect of Cyclophosphamide on Chromosomes." In Fish Analysis for Drug and Chemicals Mediated Cellular Toxicity. Springer Singapore, 2020. http://dx.doi.org/10.1007/978-981-15-4700-3_2.
Full textMulisch, Hans-Martin, Werner Winter, and Hermann H. Dieter. "Assessment of the Effect Potential of Environmental Chemicals." In Exposure and Risk Assessment of Chemical Pollution — Contemporary Methodology. Springer Netherlands, 2009. http://dx.doi.org/10.1007/978-90-481-2335-3_9.
Full textConference papers on the topic "Earthworms – Effect of chemicals on"
Kniuipytė, Inesa, Marius Praspaliauskas, Jūratė Žaltauskaitė, and Austra Dikšaitytė. "Bioremediation Efficiency of Heavy Metal Contaminated Soil Using Earthworm Eisenia Fetida." In 11th International Conference “Environmental Engineering”. VGTU Technika, 2020. http://dx.doi.org/10.3846/enviro.2020.593.
Full textHala I Chaoui, Patrick Topper, Robert E Graves, Mary Ann Bruns, and Thomas L Richard. "The effect of compost and earthworms casts biofilters on gaseous emissions from dairy manure stacks." In 2007 Minneapolis, Minnesota, June 17-20, 2007. American Society of Agricultural and Biological Engineers, 2007. http://dx.doi.org/10.13031/2013.24408.
Full textArbab, M. Hassan, Antao Chen, Eric I. Thorsos, Dale P. Winebrenner, and Lisa M. Zurk. "Effect of surface scattering on terahertz time domain spectroscopy of chemicals." In Integrated Optoelectronic Devices 2008, edited by Kurt J. Linden and Laurence P. Sadwick. SPIE, 2008. http://dx.doi.org/10.1117/12.769015.
Full textYuce, H. H., A. D. Hasse, and P. L. Key. "Effect Of Common Chemicals On The Mechanical Properties Of Optical Fibers." In O-E/Fiber LASE '88, edited by Roger A. Greenwell, Dilip K. Paul, and Shekhar G. Wadekar. SPIE, 1989. http://dx.doi.org/10.1117/12.960047.
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Full textXie, Qianyan, Debra Yeager, and Jack Chu. "The Effect of Chemicals and Solvents on Plastics -An Engineering Practice Guide." In International Congress & Exposition. SAE International, 1995. http://dx.doi.org/10.4271/950634.
Full textKirk, Joseph W., and Romony E. Sin. "Laboratory Evaluation of the Effect of Treating Chemicals on Scale Inhibitor Performance." In SPE Annual Technical Conference and Exhibition. Society of Petroleum Engineers, 1997. http://dx.doi.org/10.2118/38800-ms.
Full textZhou, Yunhe, Xiaodong Cheng, Leilei Wang, Guopu Wang, and Yong Huang. "Effect of Endocrine Disrupting Chemicals in Water Environment on Adolescent Idiopathic Scoliosis." In 2010 4th International Conference on Bioinformatics and Biomedical Engineering (iCBBE). IEEE, 2010. http://dx.doi.org/10.1109/icbbe.2010.5516586.
Full textLee, Han-Shin, Jaehyuck Choi, DonGun Lee, et al. "Effect of EUV exposure upon surface residual chemicals on EUV mask surface." In Photomask and NGL Mask Technology XVII, edited by Kunihiro Hosono. SPIE, 2010. http://dx.doi.org/10.1117/12.868292.
Full textHessling, J., and S. Shuler. "Effect of De-Icing Chemicals on Crack Sealant Performance in Colorado, USA." In GeoHunan International Conference 2009. American Society of Civil Engineers, 2009. http://dx.doi.org/10.1061/41043(350)14.
Full textReports on the topic "Earthworms – Effect of chemicals on"
Lorenz, P. B. The effect of alkaline agents on retention of EOR chemicals. Office of Scientific and Technical Information (OSTI), 1991. http://dx.doi.org/10.2172/5629326.
Full textPetit, Sylvain, Joannie Chin, Amanda Forster, Michael Riley, and Kirk Rice. Effect of artificial perspiration and cleaning chemicals on mechanical and chemical properties of ballistic fibers. National Institute of Standards and Technology, 2008. http://dx.doi.org/10.6028/nist.ir.7494.
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