scholarly journals The impact of ultrasonic power and time for the removal of Total Petroleum Hydrocarbon from low permeability contaminated soils

2019 ◽  
Vol 314 ◽  
pp. 012005
Author(s):  
Agus Jatnika Effendi ◽  
Marita Wulandari
Keyword(s):  
Contaminated Soils ◽  
Petroleum Hydrocarbon ◽  
Total Petroleum Hydrocarbon ◽  
Low Permeability ◽  
Ultrasonic Power ◽  
The Impact

scholarly journals The impact of ultrasonic power and time for the removal of Total Petroleum Hydrocarbon from Low permeability contaminated soils

2019 ◽  
Author(s):  
agus jatnika effendi ◽  
Marita Wulandari
Keyword(s):  
Contaminated Soil ◽  
Contaminated Soils ◽  
Low Permeability ◽  
Ultrasonic Power ◽  
Optimum Conditions ◽  
Desorption Process ◽  
Central Java ◽  
Time Test ◽  
Alternative Techniques ◽  
The Impact

Alternative techniques for treated contaminated soil are physical chemicals and one of them with ultrasonic irradiation. Ultrasonic is widely studied in soil or sediment with several types of contaminants, both heavy metals and organic matter. According to previous research, ultrasonic power not only increases the desorption process or leaching contaminants from the soil but also plays an important role in the formation of radicals (•OH) which are oxidizers involved in the oxidation process. The main reactor has a dimension of 21 cm × 21 cm × 18 cm. The system used is a bath system, where the transducer is attached under the bath (reactor) so that it indirectly produces sonication. Contaminated soil has low permeability and obtained from conventional former petroleum mining land in Grobogan Regency, Central Java with initial concentrations of TPH and oil & grease of 334100 mg / kg and 87700 mg / kg. Based on optimum time test, it can be seen that the decrease in TPH was significant at the initial 15 minutes of sonication while the rest was relatively stable. At optimum conditions, TPH decreases efficiency at a frequency of 48 kHz at a soil / liquid ratio of 1: 9 (gr / ml) and a power of 160 watts is 61.03%

scholarly journals Biodegradation Potentials of Aspergillus sydowii and Fusarium lichenicola on Total Petroleum Hydrocarbon in an Oilfield Wastewater in Rivers State

2020 ◽  
pp. 1-7
Author(s):  
Williams, Janet Olufunmilayo ◽  
Aleruchi Owhonka
Keyword(s):  
Mixed Culture ◽  
Contaminated Soils ◽  
Petroleum Hydrocarbons ◽  
Petroleum Hydrocarbon ◽  
Total Petroleum Hydrocarbon ◽  
Total Petroleum Hydrocarbons ◽  
Aspergillus Sydowii ◽  
Significant Difference ◽  
Set Up ◽  
Rivers State

This study investigated the potential of Aspergillus sydowii and Fusarium lichenicola as mixed cultures in the biodegradation of Total Petroleum Hydrocarbons TPHs in oilfield wastewater. Oilfield wastewater was collected from an onshore oil producing platform and biodegradation of total petroleum hydrocarbons was investigated using standard methods. Fungi were isolated from oilfield wastewater contaminated soils obtained from the vicinity of the oil producing platform. Experimental control set-up and treatment with mixed culture of fungal isolates were periodically analyzed on days 7 and 21 intervals for total petroleum hydrocarbon degradation using Gas Chromatography (GC). The total amount of TPHs on day 1 recorded 381. 871 mg/l.  The amount of TPHs on days 7 and 21 in the mixed culture of fungi was 108.975 mg/l and 21.105 mg/l respectively while TPHs in control was 342.891 mg/l and 240.749 mg/l respectively. There was a significant difference between the mixed culture and the control on days 7 and 21 at p≤0.05. The results therefore revealed actual and significant reduction of TPHs in the mixed culture. In addition, there was clearance of n-alkanes by the mixed culture. This suggests that fungi have great potentials in biodegradation of TPHs and in remediation of TPH contaminated environments.

scholarly journals FITOREMEDIASI TANAH TERKONTAMINASI MINYAK BUMI DENGAN MENGGUNAKAN TANAMAN RUMPUT BAHIA (Paspalum notatum)

2021 ◽  
Vol 15 (1) ◽  
pp. 1
Author(s):  
Teddy Irawan ◽  
Bintal Amin ◽  
Sofia Anita
Keyword(s):  
Economic Impact ◽  
Contaminated Soils ◽  
Petroleum Hydrocarbon ◽  
Positive Impact ◽  
Local Communities ◽  
Total Petroleum Hydrocarbon ◽  
Environmental Damage ◽  
Petroleum Waste ◽  
Bahia Grass ◽  
Socio Economic Impact

The increasing need for fuel derived from petroleum is also in line with the increased exploration and production activities of petroleum. Besides producing crude oil products, this activity also produces petroleum waste. This waste will pollute the soil which will have an impact on environmental damage, disruption of human health and other living things. Therefore according to Veegha (2008), an efficient and environmentally friendly method for treating petroleum waste is needed. One of the waste treatment methods is using phytoremediation method. Phytoremediation is defined as a technology for cleaning, removing or reducing harmful pollutants, such as heavy metals, pesticides, and toxic organic compounds in soil or water using the help of plants. This research was conducted for three months from September to November 2019 at the open nursery of PT. CPI with paranet shade 60%. This study aims to determine the effectiveness of bahia grass (P. notatum) in degrading Total Petroleum Hydrocarbon (TPH) in petroleum-contaminated soils in the Rokan Block PT. Chevron Pacific Indonesia and analyze the socio-economic impact of phytoremediation on local communities. The results showed that the effectiveness of Bahia (P. notatum) grass proved effective in reducing the concentration of Total Petroleum Hydrocarbon (TPH) in petroleum-contaminated soils in the Rokan Block operating area of PT. Chevron Pacific Indonesia. The percentage of effectiveness shows a decrease in value of up to 58.38%. The socio-economic impact of phytoremediation on local communities has a positive impact with the planned phytoremediation activities using bahia grass with the community as work agents for planting the grass.

Hydrocarbon treatability study of Antarctica soil with Fenton’s reagent

2021 ◽  
Author(s):  
Samuel Beal ◽  
Ashley Mossell ◽  
Jay Clausen
Keyword(s):  
Environmental Health ◽  
Contaminated Soil ◽  
Contaminated Soils ◽  
Petroleum Hydrocarbon ◽  
Total Petroleum Hydrocarbon ◽  
Fenton’S Reagent ◽  
Fenton's Reagent ◽  
Mcmurdo Station ◽  
Petroleum Contaminated Soil ◽  
Annual International Conference

The study objectives were to determine the effectiveness of Fenton’s Reagent and Modified Fenton’s Reagent in reducing Total Petroleum Hydrocarbon (TPH) concentrations in petroleum-contaminated soil from McMurdo Station, Antarctica. Comparisons of the contaminated soils were made, and a treatability study was completed and documented. This material was presented at the Association for Environmental Health and Sciences Foundation (AEHS) 30th Annual International Conference on Soil, Water, Energy, and Air (Virtual) on March 25, 2021.

scholarly journals Enhancing the Phytoremediation of Hydrocarbon-Contaminated Soils in the Sudd Wetlands, South Sudan, Using Organic Manure

2020 ◽  
Vol 2020 ◽  
pp. 1-8 ◽  
Author(s):  
J. A. Ruley ◽  
A. Amoding ◽  
J. B. Tumuhairwe ◽  
T. A. Basamba ◽  
E. Opolot ◽  
...  
Keyword(s):  
Natural Attenuation ◽  
Contaminated Soils ◽  
Petroleum Hydrocarbon ◽  
South Sudan ◽  
Organic Manure ◽  
Total Petroleum Hydrocarbon ◽  
Cow Dung ◽  
Tithonia Diversifolia ◽  
Treatment Combination ◽  
Hyparrhenia Rufa

Phytoremediation of hydrocarbon-contaminated soils is a challenging process. In an effort to enhance phytoremediation, soil was artificially contaminated with known concentration of light crude oil containing Total petroleum hydrocarbon (TPH) at a concentration of 75 gkg−1 soil. The contaminated soil was subjected to phytoremediation trial using four plant species (Oryza longistaminata, Sorghum arundinaceum, Tithonia diversifolia, and Hyparrhenia rufa) plus no plant used as control for natural attenuation. These phytoremediators were amended with concentrations (0, 5 and 10 gkg−1 soil) of organic manure (cow dung). Results at 120 days after planting, showed that application of manure at concentrations of 5 and 10 gkg−1 soil combined with an efficient phytoremediator can significantly enhance reduction of TPH compared to natural attenuation or use of either manure or a phytoremediator alone (p<0.05). The study also showed that a treatment combination of manure 5 gkg−1 soil, with a phytoremediator gives a similar mean percentage reduction of TPH as manure 10 gkg−1 soil (p>0.05). Therefore, the study concludes that use of phytoremediators and manure 5 gkg−1 soil could promote the restoration of TPH contaminated-soils in the Sudd region of South Sudan.

scholarly journals Biotreatment of Crude Oil Contaminated Soil

2019 ◽  
pp. 1-9 ◽  
Author(s):  
B. M. Popoola ◽  
A. A. Olanbiwonninu
Keyword(s):  
Crude Oil ◽  
Contaminated Soil ◽  
Contaminated Soils ◽  
Petroleum Hydrocarbon ◽  
Soil Samples ◽  
Total Petroleum Hydrocarbon ◽  
Available Phosphorus ◽  
Subsequent Increase ◽  
A Value ◽  
Treatment Measures

Biodegradation of hydrocarbons by microorganisms represents one of the primary mechanisms by which petroleum and other hydrogen pollutants are eliminated from the environment. This work was carried out on the effect of microorganisms on the biotreatment of oil in crude oil contaminated soil. Microorganisms were isolated from two experimental soil samples contaminated with Bonny Crude and normal uncontaminated soil as a control over a period of seven months. The microbial as well as the physico-chemical parameters of the soil samples were all analyzed using standard methods. Changes in total petroleum hydrocarbon level were measured appropriately. Treatments used were the microbial isolates. Forty-four microorganisms were isolated from the contaminated soils and identified as species of Pseudomonas (7), Flavobacterium (6), Bacillus (8), Proteus (4), Klebsiella (1), Pencillium (5), Aspergillus (7), Fusarium (3), Trichypton (2) and Neurospora (1). Ten of the forty-four isolates had ability to degrade crude oil in the laboratory. On contamination a value of 1.0X105 cfu/g in microbial counts were obtained followed by a subsequent increase in population levels after a period of 2months with a value of 1.0X106 cfu/g. Oil application to the soil resulted in an increase in total petroleum hydrocarbon from 0.31 ppm to 5.53 ppm; organic matter from 0.41% to 7.34%; available phosphorus from 1.75 ppm to 2.84 ppm. The treatment measures all showed progressive decrease in oil concentration in the soil. Mixture of bacterial and fungal isolates as a treatment measure proved to be more favourable above all others, it brought the concentration from 5.53 ppm to 0.31 ppm after a period of 5 weeks of treatment, which is same value with the normal soil (uncontaminated). Species of Pseudomonas, Bacillus, Flavobacterium, Proteus, Klebsiella, Penicillium, Aspergillus, Fusarium, Trichyphyton and Neurospora had potential for the degradation of bonny crude oil. They could therefore be employed in environmental cleanup of petroleum spill site.

scholarly journals Myco-enhanced Bioremediation in Open Field Crude Oil Contaminated Soil Using Mucor racemosus and Aspergillus niger

2021 ◽  
pp. 119-141
Author(s):  
O. Ule ◽  
D. N. Ogbonna ◽  
R. N. Okparanma ◽  
R. R. Nrior
Keyword(s):  
Aspergillus Niger ◽  
Crude Oil ◽  
Open Field ◽  
Contaminated Soils ◽  
Petroleum Hydrocarbon ◽  
Polluted Soil ◽  
Total Petroleum Hydrocarbon ◽  
Mucor Racemosus ◽  
Rivers State ◽  
Hydrocarbon Utilizing Bacteria

Aim: To assess the Mycoremediation potential of Mucor racemosus and Aspergillus niger in open field crude oil contaminated soils in Rivers State, Nigeria.  Study Design: The study employs experimental design, statistical analysis of the data and interpretation. Place and Duration of Study: Rivers State University demonstration farmland in Nkpolu-Oroworukwo, Mile 3 Diobu area of Port Harcourt, was used for this study. The piece of land is situated at Longitude 4°48’18.50” N and Latitude 6ᵒ58’39.12” E measuring 5.4864 m x 5.1816 m with a total area of 28.4283 square meter. Mycoremediation process monitoring lasted for 56 days, analyses were carried out weekly at 7 days’ interval. Methodology: Five (5) experimental plots were employed using a Randomized Block Design each having dimensions of 100 x 50 x 30 cm (Length x Breadth x Height) and were formed and mapped out on agricultural soil, each plot was contaminated with 22122.25g of Crude Oil except Control 1 and left fallow for 6 days after contamination for proper contamination and exposure to natural environmental factors to mimic crude oil spill site. On the seventh day bio-augmentation process commenced using two (2) fungal isolates namely Aspergillus niger [Asp] and Mucor rasemosus [Muc]). Two (2) control plots (P1: Uncontaminated and unamended soil - CTRL 1 US) and P2: Crude Oil contaminated but unamended soil - CTRL 2 CS); P3 = P5 were contaminated and amended/bioaugmented (P3: CS+Asp, P4: CS+Muc, P5: CS+Asp+Muc respectively. Soil profile before and after contamination was assayed while parameters like Temperature, pH, Nitrogen, Phosphorus, Potassium and Total Petroleum Hydrocarbon (TPH) contents were monitored throughout the experimental period. Microbial analyses such as Total Heterotrophic Bacteria (THB), Total Heterotrophic Fungi (THF), Hydrocarbon Utilizing Bacteria (HUB) and Hydrocarbon Utilizing Fungi (HUF) were recorded. Bioremediation efficiency was estimated from percentage (%) reduction of Total Petroleum Hydrocarbon (TPH) from day 1 to the residual hydrocarbon at day 56 of bio- augmentation/ biostimulation plots with the control. Results: Results revealed actual amount of remediated hydrocarbon and % Bioremediation Efficiency at 56 days in the different treatment plots (initial TPH contamination value of 8729.00mg/kg) in a decreasing order as follows: CS+Muc (8599.19mg/kg; 33.66%) > CS+Asp+Muc (8357.31mg/kg; 33.04%) > CS+Asp (8341.58mg/kg; 32.98%) > CTRL 2 -CS (Polluted soil without amendment) (81.06mg/kg; 0.32%). Microbiological results After fifty-six (56) days of bioremediation monitoring; %HUB were as follows; CS+Asp+Muc (45.30%) > CS+Asp (40.32%) > CS+Muc (35.01%) > CTRL 2 –CS (30.43%) > CTRL 1 – US (0%). These results indicate that the presence of the contaminated crude oil stimulated and sustained the growth of Hydrocarbon Utilizing Bacteria (HUB) in the contaminated plots (P2 - P3); more so, the higher growth in the enhanced bio-augmented plots (P3 – P5) shows the positive impact of fungal bio-augmentation in bioremediation of crude oil polluted soil. It was further observed that treatment plots with higher HUB or HUF had higher percentage (%) bioremediation efficiency; that is, the higher the sustained HUB and HUF population, the higher the %Bioremediation process. Hydrocarbon Utilizing Bacteria (Log10 CFU/g): CS+Asp (4.20) (Day 35) > CS+Muc+Asp (4.18) (Day 35) > CS+Muc (4.08) (Day 28) > CTRL 2 – CS (3.95) (Day 21) > CTRL 1 – US (3.78) (Day 35). (Fig. 3). Hydrocarbon Utilizing Fungi (Log10 CFU/g): CS+Asp (4.68) (Day 35) > CS+Muc+Asp (4.58) (Day 35) > CS+Muc (4.48) (Day 35) > CTRL 2 – CS (4.23) (Day 21) > CTRL 1 – US (2.85) (Day 42). Conclusion: Study showed that bioremediation of crude oil-contaminated soils with Bioaugmenting fungus singly may be more effective than combination with others depending on the type of substrate used, nature of the hydrocarbon utilizing organism and environmental conditions prevalent as seen in Mucor racemosus having higher bioremediation potential than when combined with Aspergillus niger. Notably, Hydrocarbon Utlilizing Bacteria (HUB) and Hydrocarbon Utilizing Fungi (HUF) which are the key players in Bioremediation has its peak count value on Day 35, this confers that nutrient renewal on bioremediation site should be at interval of 35 days for continuous effective bioremediation of hydrocarbon pollutants. It is therefore recommended that single microbes of high bioremediation potential could be used since its more effective than consortium of many hydrocarbon utilizing microbes. Also, nutrient or bio-augmenting microbes’ renewal on bioremediation site should be at an interval of 35 days for continuous effective bioremediation of hydrocarbon pollutants.

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