Showing posts sorted by date for query Kenaf. Sort by relevance Show all posts
Showing posts sorted by date for query Kenaf. Sort by relevance Show all posts

Tuesday, February 14, 2023

Water Pollution Cleanup with Hemp

 OHIO 🚨 Woman finds all her chickens dead 10 miles from East Palestine, Ohio
#OhioTrainDisaster #OhioRiver



There are solutions to pollution. The Ohio Train Derailment and the toxins that are being reported on the Ohio River can be cleaned up. Here are examples of removing chemicals from water with modified hemp core.

Why is it so hard to work with the EPA?  I've been trying for years? Their silence is deafening.


 


 

We are The Pollution Solution The Goal of the Pollution Solution is to turn toxins and contaminants into $$ cash to offset the cost of remediation of cleanup projects which will allow for future use of the property that will not pose a health danger to People, Animals, and the Ecosystem.
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Saturday, September 26, 2020

Kenaf Hibiscus Cannabinus L for Phytoremediation -Science Studies-

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Sunday, December 30, 2018

Uranium Water Biofilter Remediation

ElectroHemp blog post on Uranium Reducing Phytoremediation Raft Design
ElectroHemp Phytoremediation Raft designs can be designed to remove any number or combination of toxic pollutants found in water sources

Previously ElectroHemp highlighted how Natural biofilters for toxic metals can be used for Pb (Lead) Removal. This same technique can be used for Uranium (U) removal. 
All that needs to be done is substitute the Raft and Plants that will extract Uranium and it's by products.
Example: A phytoremediation raft can be constructed with these biosorbing products: Tree Bark (Pinus, Acacia), Agro Wastes (Tea Leaves, Rice Hulls) Apple Wastes . With these type of hyperaccumulating plant species: Hemp, Kenaf, Sun Flowers, Mustard Grass, Rape, even some Grasses 
To ensure all the Toxic Contamination comes in contact with the Raft and Plant Roots growing on the Phytoremediation Rafts that phytoextract the toxins. ElectroHemps uses Electrokinetics into the Remediation removal process. Electrokinetics draws toxins where directed.
ElectroHemps combines Electrokinetics, Phytoremediation, and Biofilters into the Remediation removal process. Key point: Electrokinetics draws toxins where directed.
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Natural biofilters for toxic metals

The following Science Paper highlights how ElectroHemp Phytoremediation Rafts can be used as Biofilters to clean pollution from water sources.
Phytoremediation Raft Infographic- Plants cycle water toxins when grown on Rafts
a wide variety of agricultural and forestry by products have been used as biosorbents of toxic metals in a bid to develop biofilters for specific applications Electronic Journal of Biotechnology: 
The added benefit of how ElectroHemp equips these rafts with Electrokinetics will actually increase the toxic contamination removal because of the forced migration of the toxins is directed towards the rafts and plants roots which growing on the Phytoremediation Rafts.
The added benefit of how ElectroHemp equips these rafts with Electrokinetics will actually increase both the toxic up take in the plants because the forced migration of the toxins is directed towards the rafts and plants roots growing on the Phytoremediation Rafts.
ElectroHemp Phytoremediation Raft designs can be designed to remove any number or combination of toxic pollutants found in water sources.

A floating phytoremediation raft constructed of: waste tea leaves, Pinus pinaster bark, Olea europea, Acacia nilotica bark. Which has these plant examples growing on it: Kenaf, Water Lettuce, Alligator Weed create a combination of Natural Solutions in the detoxification of Lead (Pb) from water. Scotty, ElectroHemp 
Phytoremediation Science Paper link
  • i) Cotton - Hg; Groundnut skins - Cu; 
  • Tree Bark (Pinus, Acacia etc.) - variety of metals; 
  • Agrowaste - variery of metals; 
  • waste tea leaves - Pb, Cd, and Zn; 
  • Pinus radiata -U; 
  • Apple waste -Variety of metals; 
  • Cellulose - Variety of metals; Rice hulls - Variety of metals; 
  • Exhausted coffee grounds - Hg; 
  • Pinus pinaster bark - Zn, Cu, Pb. Saw mill dust (wood waste)- Cr; 
  • Freshwater green algae - variety of metals; 
  • Marine algae- Pb, Ni; 
  • ii) Sphagnum (moss peat) - Cr(VI); 
  • iii) Immobilized Aspergillus niger, A. oryzae - Cd, Cu, Pb, and Ni ; 
  • Olive mill waste Olea europea Cr, Ni, Pb, Cd, and Zn, Cu and Ni; 
  • Streptomyces rimosus (bacteria); 
  • Saccharomyces cerevisiae (yeast); 
  • Penicillium chrysogenum (fungi), Fuscus vesiculosus and Ascophyllum nodosum (marine algae) Zn, Cu andNi; Phanerochaete chrysosporium, P. versicolar - Pb, Ni, Cr, Cd, Cu; Pinus radiata - U;
  • Immobilized Pseudomonas putida 5-X and Aspergillus niger, Mucor rouxxi - Cu; 
  • Actionomycetes, Aspergillus niger, A.oryzae, Rhizopus arrhizus, R. nigricans- Cd; Rhizopus arrhizus - Cr(VI), Pb; Rhizopus nigricans, Phanarochaete chrysogenum -Pb; Aspergillus niger and Rhizopus arrhizus - Ni 

 Acacia nilotica bark serves as an adsorbent of toxic metals. Bark (1 g) when added to 100 ml of aqueous solution containing 10 mg ml-1 metal solution exhibited different metal adsorption values for different metals. The order of metal adsorption being Cr > Ni > Cu > Cd> As > Pb. A similar trend of metal adsorption was observed when the bark is reused (1strecycle) Cr > Ni > Cu > Cd > Pb and also in the column-sorption. In order to verify the metal removal property of A. nilotica bark, toxicity bioassay with Salix viminalis stem cuttings in hydroponic system augmented with Cd, Cr and Pb together with A. nilotica bark powder was carried out. The results of toxicity bioassay confirmed the metal adsorption property of the bark powder. The functions of toxicity studies include leaf area, root length and number of new root primordia produced per stump. The leaf area, root length and number of new root primordia increased considerably in the presence of A. nilotica bark. The order of metal toxicity for leaf area and new root primordial is Cd > Cr > Pb. However, for root length the order of metal toxicity is Cr > Cd > Pb. The metal budgets of the leaf and root confirmed that the bark powder had adsorbed substantial amount of toxic metals and thus, alleviates the toxicity imposed by the various tested elements (Prasad et al. 2001).

 Quercus ilex L. phytomass from stem, leaf and root as adsorbent of chromium, nickel, copper, cadmium and lead at ambient temperature was investigated. The metal uptake capacity of the root for different metals was found to be in the order of: Ni > Cd > Pb > Cu > Cr; stem Ni > Pb> Cu > Cd > Cr and leaf Ni > Cd > Cu > Pb > Cr. The highest amount adsorbed was Ni (root > leaf > stem). Data from this laboratory demonstrated that Ni is mostly sequestered in the roots where concentrations can be as high as 7.30 nmol/g dry weight, when one year old seedlings were treated with Ni (2000 mg/l) in pot culture experiments, compared to 0.13 nmol/g dry weight, in the control. This proves that the root biomass of Q. ilex has the capacity for complexing Ni. Chromium exhibited the least adsorption values for all the three types of phytomass compared to other metals. The trend of adsorption of the phytomass was similar for nickel and cadmium i.e. root > leaf > stem. Desorption with 10 mM Na2 EDTA was effective (55-90%). Hence, there exists the possibility of recycling the phytomass. The biosorption results of recycled phytomass suggests, that the selected adsorbents are reusable (Prasad and Freitas, 2000).
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Wednesday, August 31, 2016

IKEAs lesser known environmental project

If only more business cared about the environment as much as IKEA does.

Most everyone has heard that the St Louis IKEA Store is powered by solar panels!  Here is a lesser known environmental project they have incorporated into the property along Forest Park and Vandeventer Streets.
The parking lot in of the St Louis IKEA store drains into a low $$$ cost natural phytoremediation filter system.

Article 1 Plants as Water Protectors blog series

The IKEA's Engineers and Crew that installed the water filtration Phytoremediation project did a seamless job of blending the bioremediation system into the natural environment.  If it wouldn't have been for my growing the Kenaf plants and seeing the unmistakable Kenaf Flowers- I may not have noticed. 

Ikea Store Flags and Kenaf Flowering Plants used modified Riparian Buffer StLouis
IKEA Store Flags and Kenaf Flowering Plants used modified Riparian Buffer StLouis 
Ikea Parking Lot drains away from the building into modified riparian buffers along Forest Park Parkway and Vandeventer
IKEA Parking Lot drains away from the building into modified riparian buffers along Forest Park Parkway and Vandeventer
Any contaminants that escape or drip from the Autos in the parking lot will eventually make their way into the modified riparian buffer zone that removes the toxins naturally
Any contaminants that escape or drip from the Autos in the parking lot will eventually make their way into the modified riparian buffer zone that removes the toxins naturally
The break in the concrete curb allows the water to enter the riparian buffer zone where the Plants naturally cycle the toxins from the water.
The break in the concrete curb allows the water to enter the riparian buffer zone where the Plants naturally cycle the toxins from the water.
Phytoremediation Plants are growing in a bed of Gravel and Rock allowing the roots of the plants direct contact with the toxins that will be removed by Phytoremediation.
Phytoremediation Plants are growing in a bed of Gravel and Rock allowing the roots of the plants direct contact with the toxins that will be removed by Phytoremediation.

 In ElectroHemps IKEAs next sustainable bioremediation post (publication date 9/1/16) I will explain with photos, diagrams, and CAD drawings how the water toxins are removed before entering the public water system.

Toxins and Contaminants are removed the Natural Way by using Plants in a process called Phytoremediation. 

https://electrohemp.blogspot.com/2017/07/citizen-science-phytoremediation.html



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Location: https://www.google.com/maps/place/IKEA+St.+Louis+Home+Furnishings/@38.633387,-90.2470636,17z/data=!3m1!4b1!4m5!3m4!1s0x87d8b4c04aa337bf:0x6041c4df2dd1e9f!8m2!3d38.633387!4d-90.2448749

Friday, June 24, 2016

Contain and Control BioRad 5 Stage Treatment Train



Contain and Control
Are major concerns when dealing with Nuclear Radiation.  
The following table demonstrates the safety avenues used in the BioRad 5 stage treatment train.



ElectroHemp Pilot Study Safety Solutions Table 1
The ElectroHemp Table 1 below demonstrates how ElectroHemp BioRad  5 Stage Treatment Train works as a system and process while addressing the safety and concerns.
Concerns
Solutions
Plant-based biological limitation
ElectroHemp System addresses these concerns

  1. Low plant tolerance
  2. Lack of contaminant
    translocation from root to
    Shoot
  3. Small size of remediating
    plants
  1. Use plants that tolerate toxins
  2. Containment central location is housed in greenhouse or hoophouse, Proper plant species selection and increased soil vitality increases translocation into the plant.
    1. If containment was concentrated in the root zone of the plant.  Removing the root systems in a field would require a “potato” type harvesting machine.  In a Greenhouse because of scale Elbow Grease and a Shovel will suffice. Disposal is same as fiber
  3. Many plant species are proven
Regulatory limitations
Phytoremediation & Electro-Horticulture is recognized solution by: EPA, FUSRAP, Governing Bodies, etc
  1. Lack of cost and performance data
  2. Regulators unfamiliarity with the technology
  3. Disposal of contaminated plant waste
  4. Risk of food chain contamination
  1. Agree Performance Data is lacking.  Disagree Cost has been determined $20,000.  Compared to other treatment systems.  Phytoremediation is the least expensive option.
  2. Agree as well as a great percentage of the Public
  3. Disposal of Contaminated waste is handled in-situ (on site) in sealed containers.
  4. Food chain contamination eliminated with project housed inside hoophouse or greenhouses
Other Limitations
Limitation Addressed
  1. Contaminant beneath root zone
  2. Lengthy process
  3. Contaminant in biologically unavailable form
  4. Lack of remediating plant species
  1. ElectroHemp directs the heavy metal toxins to a central point located in a Greenhouse, Hoophouse, Fenced in or protected area- where plants phyto-extract the toxins.
  2. Electro-Horticulture
    1. increases soil vitality and heavy metal movement- which allows plants to grow bigger, healthier, and cycle more toxins from the soil.
    2. By utilizing Indoor Grow operations increases growing opportunities: length of growing seasons and increases the use of plant species not suited to existing climates.  
    3. 3 plant cycle rotations per year minimum, with the possibilities of 3-6 forage harvest opportunities (dual cutting)
  3. bioavailability of heavy metals in soil can also be increased by adding chelating agents such as EDTA, ammonium sulfate, critic acid and elemental sulfur, mulch, and erosion control in addition to Electrokinetics.
  4. Hemp, Kenaf, Rape, Sunflowers, and  many other species and strains of plants will perform the needed phytoremediation techniques desired.  Note: Greenhouse/Hoophouse give additional options for greater adoption of plant species.

Ref: The Use of Plants for the Removal of Toxic Metals from Contaminated Soil
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