Thursday, February 28, 2019

STL Bioremediation and Erosion Control


Those black snake looking net tubes that are used to control erosion are also bioremediation filters.

These images are from the same  area of StLouis with the 3 Basin Water Pollution and Filtration setup that cleans pollution from water runoff from a stlouis city street and building parking lots.

Here's some close up images showing how well these dentrifying bioremediation systems work when placed at or near ground level.







The erosion control filters are performing an outstanding job.








Notice the uphill side in the images above, the soil and organic matter is building up? This proves the filters are trapping the soil runnoff before it travels into the waterway below.



Yes those are wood chips in the black snake netting

This also means any contaminants in the water runnoff are also filtered in this modified dentrifying biofilter.






Sunday, February 17, 2019

StL Plants As Water Protectors

Recently I was in a suburb of StLouis City and happened across this 3 Basin Water Pollution and Filtration setup that cleans pollution from water runoff from a stlouis city street and building parking lots.


Bioremediation and Phytoremediation are the 2 forms of water pollution filtration and cleanup used in this real life St.Louis example. The microbes are the workhorses with this bioremediation system.

A site inspection revealed a 3 level catch basin design. Each catch basin draining into the "downhill" basin below. Each water catch basin also appears to be geared for different contaminant and toxin removal.

Middle Water Filtration Catch Basin

Middle Water Filtration Catch Basin

Upper Water Filtration Catch Basin



Gravel Base Middle Basin

small gravel bioremediation filtration

Each water basin allows the time needed for the toxins and contaminants the opportunity to mingle and the microbes and plant roots. 

This allows the microbes a homebase to feast and break down the contaminants and plant roots the time needed to phytoextract contaminants.

The middle basin with the gravel base is very similar to how a sand filtration system works in a fish tank. The gravel and rocks provide a safe home for the microbes to thrive.

The microbes are the workhorses with this bioremediation system.


Saturday, February 2, 2019

Lessoning Agriculture Field Water Runnoff Pollution

 Agriculture contaminants is one of the 3 pollution sources quoted in EWG's Tap Water Database: Pollution Sources and is one reason ElectroHemp has been sharing ways farmers can use buffer zones, filter strips with phytoremediation to lesson field pollution runoff scenarios.

Agriculture

Agricultural activities are one of the main sources of water pollution for U.S. rivers, streams, lakes, wetlands and groundwater. Each year, farm operators apply more than 12 million tons of nitrogen fertilizer and 8 million tons of phosphorous fertilizer to cropland, some of which runs off into water sources.


Manure is another important source of water contamination. It’s estimated that livestock produce up to 1 billion tons of manure each year, and runoff from farms and feedlots can be laden with sediments and disease-causing microorganisms. And many pesticides have no federally mandated limits for drinking water, which means utilities and their customers have no benchmark to know if the amount of a specific pesticide in water is safe.



Many water utilities in farm country are forced to treat water supplies to remove agriculture-related pollutants, often relying on expensive processes such as carbon treatment and ion exchange. Despite utilities' efforts, agricultural contaminants are detected in the drinking water served to millions of Americans each year.


Source: EWG's Tap Water Database: Pollution Sources




Sunday, January 20, 2019

Guest Scotty, from St. Louis - Electro-Phytoremediation Process 8-22-2016


Updated information after phone conversation with person planning phytoremediation project to use hemp to phytoextract toxins from soil.

Is this the video you mentioned? https://youtu.be/pVVWcd9bXrA  the video below explains why not everyone should be able to do this UNTIL the system is proven safe.

   I am not afraid of exposing corruption and shortsightedness everywhere I find it.  

I'll be doing another radio interview this coming week sometime about the electrohemp system.

Lonnie Simpson is interviewer. She's anti nuke, understands plight of downwinders being exposed to contamination and all the health issues.

She mentioned the latest stuff I've pieced together that is wanted by Dept of Defense in re to uranium is dangerous for my safety. I'm not worried or scared and I'm going to share this to the world. (In addition to I have found a buyer in the health industry for the decontaminated material)

If you researched EPA suggestions you'd realize they have a goal of turning toxins into cash to offset remediation costs.  My end disposal options do this in 2 or more ways. Instead of the costly glass infusion you mentioned.
https://www.epa.gov/risk/calculating-preliminary-remediation-goals-prgs


FYI: Paul with Fungi Perfecti informed me: mushrooms will decontaminate nuke rads, but mushrooms still need to be picked up and disposed of [or else the contamination will be reintroduced back into the environment].

Here's the info I shared with the World Wide Hemp group I'm a part of.


 https://facebook.com/HempEnvironmentalForum/?

Lonnie also clued me in on the grant writer who won't consider the organic remediation disposal vs nuke ind suggestions.


It should be pretty interesting interview. She's hip to the nuke ind tactics / shortsighted activist etc.


Fyi: i am not going to mention your name or location but I am going to expose what I feel is shortsighted science because you won't or haven't researched a true solution on this issue.


I'll send more info when we hash out an interview time and where to view it.

Peace,
Scotty


Saturday, January 19, 2019

Cannabis Phytoremediation Science Paper

Cannabis sativa L. growing on heavy metal contaminated soil: Growth, cadmium uptake and photosynthesis
Linger, P., Ostwald, A., Haensler, J.
a) Physiological Chemistry of Plants, Dept. C - Mathematics and Science, Bergische University of Wuppertal, Gauss Str. 20, D-42097 Wuppertal, Germany
a) Geobotany, Heinrich-Heine-University, Universitatsstr. 1, D-40225 Düsseldorf, Germany
Abstract
The effects of different cadmium concentrations [17 mg(Cd) kg -1(soil) and 72 mg(Cd) kg- 1(soil)] on Cannabis sativa L. growth and photosynthesis were examined. Hemp roots showed a high tolerance to Cd, i.e. more than 800 mg(Cd) kg-1(d.m.) in roots had no major effect on hemp growth, whereas in leaves and stems concentrations of 50 - 100 mg(Cd) kg-1(d.m.) had a strong effect on plant viability and vitality. For control of heavy metal uptake and xylem loading in hemp roots, the soil pH plays a central role. Photosynthetic performance and regulation of light energy consumption were analysed using chlorophyll fluorescence analysis. Seasonal changes in photosynthetic performance were visible in control plants and plants growing on soil with 17 mg(Cd) kg-1(soil). Energy distribution in photosystem 2 is regulated in low and high energy phases that allow optimal use of light and protect photosystem 2 from overexcitation, respectively. Photosynthesis and energy dissipation were negatively influenced by 72 mg(Cd) kg-1(soil). Cd had detrimental effects on chlorophyll synthesis, water splitting apparatus, reaction centre, antenna and energy distribution of PS 2. Under moderate cadmium concentrations, i.e. 17 mg(Cd) kg -1(soil), hemp could preserve growth as well as the photosynthesis apparatus, and long-term acclimation to chronically Cd stress occurred.

Tuesday, January 15, 2019

An Asian grass can be the key to removing lead from contaminated soil

An Asian grass can be the key to removing lead from contaminated soil:
Sewan grass (Lasiurus scindicus Henrard) is a perennial grass that can live up to 20 years. It is a bushy, multi-branched desert grass with ascending to erect wiry stems, up to a height of 1-1.6 m, and a stout woody rhizome (FAO, 2010; Ecocrop, 2010). Leaves are alternate with a thin leaf-blade. The inflorescence is a silky, 10 cm long raceme bearing hairy spikelets. The fruit is a caryopsis (Anon., 2010; eFloras, 2010; FAO, 2010; Burkill, 1985).

Sewan grass forms bushy thickets in sandy deserts where it is used for pasture, hay and fodder for livestock. This grazing pasture is of outmost importance in areas where annual rainfall is below 250 mm (Ecocrop, 2010). It is relished by ruminants but does not stand heavy grazing and disappears when overgrazed (El-Keblawy et al., 2009).

Modern agricultural practices have left long-lasting environmental damage, but the latest trend in scientific research – which looks for natural ways of reversing this damage – is hopeful.

Research from JECRC University in India is no exception, as they found a process which restores soil that has been polluted with lead. The study, published in the American […] For the study, researchers utilized phytoremediation to remove the lead from contaminated soil.
Defined as “the efficient use of plants to remove, detoxify or immobilize environmental contaminants in a growth matrix (soil, water or sediments) through the natural biological, chemical or physical activities and processes of the plant,” the procedure refers to a number of technologies that use plants to remove both organic and inorganic contaminants in soil and water.

 In this procedure, plants are grown in polluted soil to either remove a contaminant, contain it in their roots, or even degrade it completely. These plants are then harvested, processed, and disposed of.


The team first collected soil and water samples that have been contaminated by lead and put these in pots in differing concentrations. They then sowed sewan grass over a 105-day pot trial period. During this time, the team regularly sampled the soil and water to evaluate the amount of heavy metal was present in the soil.



Based on the findings, the researchers discovered that lead adversely affected the growth of sewan grass from the experiment. However, they also found that it was receptive to the lead and that the roots had accumulated it. During the samples, they found increased concentrations of lead in the roots on the 45th and 65th day after exposure.



“The lead accumulation in Lasiurus scindicus (mostly in its roots) confirming its potentiality as a phytoremediator and due to polluted soil pH high amount of lead accumulated in root compare to [the leaves],” the researchers concluded. They also looked at the potential of the grass to be further developed to restore lead-polluted soil.






Phytomining: Plant biomass containing accumulated heavy metals can be combusted to get energy and the remaining ash is considered as ‘‘bio-ore’’.

Phytomining: Plant biomass containing accumulated heavy metals can be combusted to get energy and the remaining ash is considered as ‘‘bio-ore’’.


This bio-ore can be processed for the recovery



An advantage of phytomining is the sale of energy from combustion of the biomass (Anderson et al., 1999). According to a field experiment conducted by Meers et al. (2010), cultivation of energy maize in the Campine region in Belgium and the Netherlands could result in the generation of


  • 30000–42 000 kWhel+th of renewable energy per hectare. 
  • By assuming the substitution of coal powered power plant, this would imply a cut of up to 21 tons ha1 y1 CO2. 
  • Processing bio-ores contributes less SOx emissions to the atmosphere because of their low sulfur contents.


Thus phytomining is an environment- and ecofriendly option as compared to the conventional extraction methods.



 However, the commercial viability of phytomining depends on many factors like the efficiency of phytoextraction and current market value of the processed metals. Phytomining has been commercially used for Ni and it is believed that it is less expensive than the conventional extraction methods. Using Alyssum murale and Alyssum corsicum, one can grow biomass containing 400 kg Ni ha1 with production costs of $250–500 ha1 . Considering Ni price of $40 kg1 (in 2006, Ni metal was trading on the London Metal Exchange at more than $40 kg1 ), Ni phytomining has become a highly profitable agricultural technology (crop value = $16 000 ha1 ) for Ni-contaminated or mineralized soils (Chaney et al., 2007). The enforcement of more strict legislation for limiting environmental pollution would make bio-based mining more attractive (Siddiqui et al., 2009).

 Source: https://www.researchgate.net/profile/Ezzat_Khan/publication/235880244_Phytoremediation_of_heavy_metals-Concepts_and_applications/links/0f317534f5734634b5000000.pdf



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