CHOOSE YOUR CURRENCY


EFFECTS OF PARTICLE SIZES ON BIOREMEDIATION OF CRUDE OIL POLLUTED SANDY SOILS

Amount: ₦5,000.00 |

Format: Ms Word |

1-5 chapters |



ABSTRACT

Bioremediation  has  been  proven  to  be  the  most  effective  method  of  cleaning  up  oil contaminated soils through the application of nutrients and microorganism to contaminated soils.  Hence,  this  research  was  aimed  at  investigating  the  effects  of  particle  sizes  on bioremediation of crude oil polluted sandy soils. Six different soil samples were sieved using the B.S sieve sizes. The sieve sizes were classified into X and Y such that X is fine to coarse sand while Y is very fine to coarse sand according to U.S Bureau and PRA (Public Roads Administration)  soil classification  system. The  soil samples were polluted  with escravous sweet  crude  oil  at  a  uniform  rate  of  concentration  under  aerobic  condition.  Treatment commenced after four days using nutrients and microorganism. Soil samples were examined for physiochemical  and  microbial characteristics     for a period of 42days. The parameters examined were: moisture content, particle size distribution,  total hydrocarbon content, soil pH,  available  nitrogen, available phosphorus,  total heterotrophic  bacteria and fungi count. The analysis of the soil characteristics throughout the remediation period showed that total heterotrophic bacteria and fungi counts increased in all the soil samples. THBC was highest in sample G for both fine to coarse sand(X) and very fine to coarse sand (Y ) with values of

250cfux105/g  and 298 cfux105/g at least values of Cu and D50  respectively.  There  was  a decrease in nitrogen,  phosphorus,  organic carbon content,  moisture content,  pH  and total hydrocarbon content.  The result of the study revealed that, the rate of hydrocarbon loss was higher in samples with less Cu and D50  values compared to  samples of higher values, an indication  that  particle  size distribution  parameters  could  be one of the factors  affecting bioremediation. The correlation coefficient(r) of THC versus Cu for fine to coarse sand(X) is

0.867         while         for        very        fine        to         coarse         sand         is         0.923.

CHAPTER ONE

1.0 INTRODUCTION

1.1 BACKGROUND OF THE STUDY

In Nigeria, particularly in the Niger Delta regions; the soils found are mostly sandy soils in shades of different colours of white, brown, grey and red. Sands are cohessionless  aggregate of  rounded,  subangular  or  angular  fragments  of  more  or  less  unaltered  rock or  mineral particles of size from 0.075 -4.75mm (Murthy,2009). The sand separates recognized are: very coarse,  coarse medium,  fine and very fine determined  from  the  particle  size distribution curve. The coefficient of uniformity which is an index value showing the average slope of grain size distribution  in a soil depends on the gradation  or distribution curve of the soil sample.  According  to  Arora  (2008),  the  larger  the  numerical  value  of  coefficient  of uniformity, the more the range of particles. Sand particles because of their size have a direct impact on the porosity of the soil.

The  high  incidence  and  frequency  of  crude  oil  spill  have  been  of  great  concern  to Environmental Engineers in Nigeria. This has given rise to intensive research to find ways and means of generating information and data required to assist in bioremediation strategies of crude oil spills.

Before any remediation  strategy can be done successfully,  a lot of information  would  be required  to  aid  the  process  (Bidemi,  2011).  This  information  is  meant  to  assist  in  the detection of and response to oil spill incidence.

Bioremediation  is a  means  of cleaning  up  contaminated  environments  by exploiting  the diverse metabolic abilities of microorganisms to convert contaminants to harmless products by mineralization, generation of carbon (IV) oxide and water, or by conversion into microbial

biomass  (Baggott,  1993;  Mentzer  and  Ebere,  1996).  In  Nigeria,  no  information  is  yet available  regarding  the  commercial  production  of fungi  or  microbial  inocula  for  use  in bioremediation of oil polluted environments.

The effectiveness of bioremediation is dependent upon physical and chemical condition as well as correct  analysis  of  the  parent  microbial  population  and  environmental  condition (Nedwell,  1999).  It  has  been  found  that  oil  is  degraded  efficiently  by  oil  oxidizing microorganism under laboratory and field condition (Grondeva et al., 1993). To enhance the natural cleaning action, special fertilizer which contains nutrients of nitrogen, phosphorus and potassium (NPK 15:15:15 fertilizer) is applied to the polluted site. Bioaugmentation process of bioremediation  may not be effective  for use  in oil spill cleanup  situation because the addition of non native organisms will often cause competition with the existing beneficial microorganisms (Zhu, etal., 2001).

Some  of the naturally occurring microbes capable of degrading petroleum hydrocarbon are Pseudomonas,    achrombacter,    arthrobacter,    bacillus,    flavobacter,    nocardia,    vibrio, connybacterium,   alcaligeu   (all  are  bacteria  organism).Yeast   and  fungi   organisms  are Aspergilium, candida, cladspotum, penicillum, rhodomia, trichodermia (Zhu, et al., 2001).

Analysis of biodegradation rate of crude oil contaminated soil using fertilizer or cow dung showed  that  fertilizer  was  a  better  nutrient  source  for  biostimulation  than  cow  dung (Obahiagbon and Audu 2000). Numerous laboratory studies on nutrient enhancement of oil degradation  by  natural  occurring  microorganism  have  concluded  that,  this  technique  is promising  for use in stimulating  oil degradation  (Amanchukwu  etal.,  1989,  Pitchard  and Coastal  1991,  Oliver  etal,  1978).  Excessive  application  of   the  fertilizer  can  lead  to accumulation of nutrients in the soil. The uncertainty about the toxicity of various fertilizer formulations  and  microbial  products  inhibit   broader  use  of  bioremediation  on  marine

shorelines (Hoff, 1993). Field application of nutrients  is influenced by temperature,  water runoff, substrate and other environmental  parameters that are neither fully understood nor easily quantified (Atlas, 1995).

The 1990 Gulf of Mexico spills clearly showed that bioremediation could not be measured in minutes or hours but over a period of days and weeks (Hoff, etal., 1993). The Puerto Rico spill of 1994 clearly showed that at warmer temperatures, bioremediation generally takes 6 weeks  while  at cooler  temperature  it spans  to  several  months.  This  simply  implies  that bioremediation  is not a fast process but a slow process. It has been found that addition of certain  nutrients  and  microorganisms  to  crude  oil contaminated  soils  fastens  the  rate  of hydrocarbon  loss a process called  bioremediation.  Obahiagbon  and Audu( 2000) in their various  researches  have  carried  out  extensive  study of  biodegradation  rate  of  crude  oil contaminated  soil using  fertilizer or cow dung and observed   that, fertilizer  was a better nutrient source for biostimulation   than cow dung. Ayotamuno and Kogbara(2006) in their study found out that, crude oil contamination of agricultural soils limits the availability of oxygen in the  soil layers and hence impedes the biodegradation process but they failed to investigate on the particle sizes of the soil layers to detect the porosity and voids.

Other notable researchers have also carried out studies on the physiochemical and microbial characteristic of various soils, but not much has been done on the effects of particle size on bioremediation.  With this as the study background,  the physical  properties,  chemical  and microbial  characteristics  of the  soil samples  were used  in  the  assessment  of the  rate  of Hydrocarbon loss at the end of remediation.

1.2                    STATEMENT OF PROBLEM

There are very few information  about the soil particle size properties  on  bioremediation. Therefore, this research is aimed at investigating on the effects of    particle size distribution parameters like; effective size diameter (d10), coefficient of uniformity (Cu) and average grain size (d50) as well as chemical  and microbial  properties of different  sandy soils and their effects on bioremediation

1.3                 SIGNIFICANCE OF STUDY

Since bioremediation process of cleaning up oil spills has proven to be an effective method but a slow process, this study is considered very important as it provides information and data about the particle sizes of sandy soils (Cu and D50) on bioremediation.  Through   intensive laboratory analysis, data generated   will be used as  reference  tool for further research on bioremediation, academic guide to students, Engineers, contractors and consultants who wish to embark on a similar project.

Statistical Method using regression analysis was used at the end of the research to show the linear relationship and correlation coefficient of the parameters with time in days.

1.4 OBJECTIVE OF STUDY

The objectives of the study is summarised thus:

      Compare  the  effects  of  particle  size  distribution  parameters  (Cu  and  D50)  on bioremediation, characterise the soil and crude oil samples used for the experiment.

      To determine the soil Physiochemical and microbial characteristics and their effects on bioremediation.

      Make comparison and discuss bioremediation results of soil samples with past related projects.

1.5            SCOPE OF STUDY

1) Review of past literature on similar project

2)  Sample collection and locations

3) Contamination of different sandy soil samples with crude oil at a uniform concentration of

4% each.

4) Laboratory analysis on Physical, Chemical and Microbial properties of the Soil samples.

5)  Combined  practice  of  bioaugmentation   and  biostimulation   process  of   remediation respectively.

6) Weekly soil sampling for laboratory analysis (0-7) days for a period of 42days.

7) Presentation and comparison of results with past related projects.

1.6   LIMITATION

Due to the different locations where the samples were got from, large quantity of disturbed sandy  soil  samples  required  for  the  experimental  work,  were  transported  to  the  Civil Engineering Laboratory of the University of Nigeria, Nsukka, this was tedious and expensive. The  non availability  of required  equipment,  reagent  and  apparatus  for  the chemical  and microbial  analysis  of  the  soil  resorted  to;  conducting  the  test  in  a Standard  Laboratory (Search Gate Laboratory Lagos, Soil Science and  Microbiology Department  UNN) which was capital intensive and tedious. Preserving and transporting the samples particularly during weekly sampling for 42days was tedious.



This material content is developed to serve as a GUIDE for students to conduct academic research


EFFECTS OF PARTICLE SIZES ON BIOREMEDIATION OF CRUDE OIL POLLUTED SANDY SOILS

NOT THE TOPIC YOU ARE LOOKING FOR?



Project 4Topics Support Team Are Always (24/7) Online To Help You With Your Project

Chat Us on WhatsApp »  09132600555

DO YOU NEED CLARIFICATION? CALL OUR HELP DESK:

   09132600555 (Country Code: +234)
 
YOU CAN REACH OUR SUPPORT TEAM VIA MAIL: [email protected]


Related Project Topics :

Choose Project Department