Blog List

Monday, 28 March 2016

How to Deep Fry Cooked Shrimp

Deep-fried shrimp has a delicate, sweet crispness that can make it irresistible. It is usually made with raw shrimp, but there is no reason you can’t deep fry cooked shrimp if you do it correctly. Overcooking shrimp will make it rubbery and tough, but frying cooked shrimp in batter helps retain moisture, and cooking it at a high temperature means the batter will crisp up quickly. Beer batters crisp faster than other kinds because of the way the alcohol reacts with the hot oil.
How to Deep Fry Cooked Shrimp
Cooked shrimp turn crispy when deep fried. Photo Credit Zedcor Wholly Owned/PhotoObjects.net/Getty Images

Step 1

Fill a deep fryer two-thirds full of canola oil or peanut oil and heat to 375 degrees.

Step 2

Fill a bowl with 2 to 3 inches of flour. Add salt and pepper for taste and mix it with your fingers.

Step 3

Add the beer slowly, whisking it into the flour until you have a thick batter.

Step 4

Coat the cooked shrimp in the beer batter and drop them into the oil as soon as it has reached 375 degrees.
Step 5
Fry the shrimp for one to two minutes or until the batter is crisp and golden.

Step 6

Scoop the shrimp with a slotted spoon and onto a plate lined with paper towels to drain.

Carrot Juice Nutrition Information

Drinking carrot juice provides you with several beneficial nutrients, including antioxidants. A 2011 study published in the “Nutrition Journal” reports that carrot juice increases the antioxidant status in your body, which may help protect you against cell damage and heart disease.
Carrot Juice Nutrition Information
Glass of carrot juice and carrots Photo Credit HandmadePictures/iStock/Getty Images

Calories

Carrot juice is not a high-calorie drink, but it does contain more calories than raw carrots. According to the USDA’s National Nutrient Database, while one portion -- or 1 cup -- of carrot juice provides 94 calories, 1 cup of grated carrots contains just 45 calories. The Dietary Guidelines for Americans 2010 suggest eating 2.5 cups per day from the vegetables group, which includes vegetable juices, when consuming a 2,000-calorie meal plan.

Carbohydrates

Although 1 cup of carrot juice does provide about 2 grams of dietary protein, the majority of the calories in carrot juice are from carbohydrates. The USDA reports that 1 cup of carrot juice contains about 22 grams of total carbohydrates -- including 2 grams of dietary fiber. The Dietary Guidelines for Americans 2010 suggest men consume 38 grams of fiber and women eat at least 25 grams of fiber each day to help reduce chronic-disease risk factors.
Vitamin A
One cup of carrot juice contains 2,256 micrograms of vitamin A, which exceeds the vitamin A recommended dietary allowance -- or RDA -- for adults. The Office of Dietary Supplements reports that the tolerable upper intake level, or maximum safe amount, of vitamin A is 3,000 micrograms per day. Therefore, if you drink 2 cups of carrot juice, you’re actually exceeding the vitamin A tolerable upper intake.

Other Nutrients

While carrot juice is known for its vitamin A content, it provides other essential nutrients as well. Carrot juice is an excellent source of potassium and vitamins C, E and K. One cup of carrot juice contains 689 milligrams of potassium and almost 3 milligrams of vitamin E -- the adequate intake level for potassium is 4,700 milligrams per day, while the RDA for vitamin E is 15 milligrams daily for adults, notes the Institute of Medicine.
www.livestrong.com

WOOD-DECAY FUNGUS

wood-decay fungus is a variety of fungus that digests moist wood, causing it to rot. Some species of wood-decay fungi attack dead wood, such as brown rot, and some, such as Armillaria (honey fungus), are parasitic and colonize living trees. Fungi that not only grow on wood but actually cause it to decay, are called lignicolousfungi. Various lignicolous fungi consume wood in various ways; for example, some attack the carbohydrates in wood and some others decay lignin. The rate of decay of wooden materials in various climates can be estimated by empirical models.
Wood decay caused by Serpula lacrymans (called true dry rot, a type of brown-rot)
Wood-decay fungi can be classified according to the type of decay that they cause. The best-known types are brown rotsoft rot, and white rot. Each produce different enzymes, can degrade different plant materials, and can colonise different environmental niches. The residual products of decomposition from fungal action have variable pH, solubility and redox potentials. Over time this residue will become incorporated in the soil and sediment, so can have a noticeable effect on the environment of that area.
Brown Rot
Brown-rot fungi break down hemicellulose and cellulose. Cellulose is broken down by hydrogen peroxide (H2O2) that is produced during the breakdown of hemicellulose. Because hydrogen peroxide is a small molecule, it can diffuse rapidly through the wood, leading to a decay that is not confined to the direct surroundings of the fungal hyphae. As a result of this type of decay, the wood shrinks, shows a brown discoloration, and cracks into roughly cubical pieces; hence the name brown rot or cubical brown rot.
Cubical brown rot on oak.
Brown rot in a dry, crumbly condition is sometimes incorrectly referred to as dry rot in general. The term brown rot replaced the general use of the term dry rot, as wood must be damp to decay, although it may become dry later. Dry rot is a generic name for certain species of brown-rot fungus.
Brown-rot fungi of particular economic importance include Serpula lacrymans (true dry rot), Fibroporia vaillantii (mine fungus), and Coniophora puteana (cellar fungus), which may attack timber in buildings. Other brown-rot fungi include the sulfur shelf, Phaeolus schweinitzii, and Fomitopsis pinicola.
Brown-rot fungal decay is characterised by extensive demethylation of lignins whereas white-rot tends to produce low yields of molecules with demethylated functional groups.
Soft Rot
Soft-rot fungi secrete cellulase from their hyphae, an enzyme that breaks down cellulose in the wood. This leads to the formation of microscopic cavities inside the wood, and sometimes to a discoloration and cracking pattern similar to brown rot. Soft-rot fungi need fixed nitrogen in order to synthesize enzymes, which they obtain either from the wood or from the environment. Examples of soft-rot-causing fungi are Chaetomium, Ceratocystis, and Kretzschmaria deusta.
Soft-rot fungi are able to colonise conditions that are too hot, cold or wet for brown or white-rot to inhabit. They can also decompose woods with high levels of compounds that are resistant to biological attack. Bark in woody plants contains a high concentration of tannin, which is difficult for fungi to decompose, and suberin which may act as a microbial barrier. The bark acts as form of protection for the more vulnerable interior of the plant. Soft-rot fungi do not tend to be able to decompose matter as effectively as white-rot fungi: they are less aggressive decomposers.
White Rot
White rots break down lignin and cellulose and commonly cause rotted wood to feel moist, soft, spongy, or stringy and appear white or yellow.
White rot on birch.
White-rot fungi break down the lignin in wood, leaving the lighter-colored cellulose behind; some of them break down both lignin and cellulose. Because white-rot fungi are able to produce enzymes, such as laccase, needed to break down lignin and other complex organic molecules, they have been investigated for use in mycoremediation applications.
There are many different enzymes that are involved in the decay of wood by white-rot fungi, some of which directly oxidize lignin. The relative abundance of phenylpropane alkyl side chains of lignin characteristically decreases when decayed by white-rot fungi. It has been reported that the oyster mushroom (Pleurotus ostreatus) preferentially decays lignin instead of polysaccharides. This is different from some other white-rot fungi, e.g., Phanerochaete chrysosporium, which shows no selectivity to lignocellulose.
White rot on oak.
Honey mushroom (Armillaria spp.) is a white-rot fungus notorious for attacking living trees. Pleurotus ostreatus and other oyster mushrooms are commonly cultivated white-rot fungi, but P. ostreatus is not parasitic and will not grow on a living tree, unless it is already dying from other causes. Other white-rot fungi include the turkey tail, artist's conch  and tinder fungus.
White-rot fungi are grown all over the world as a source of food - for example the Shiitake mushroom, which in 2003 comprised approximately 25% of total mushroom production.
References

  1. ^ Viitanen, T. et al. (2010). Towards modelling of decay risk of wooden materials. European Journal of Wood and Wood Products 68:303-313.
  2. a b c d J. Deacon, Wood decay and wood-rotting fungi. University of Edinburgh (2005?).
  3. a b c Microorganisms causing decay in trees and wood  University of Minnesota.
  4. a b c Vane, C. H., et al. (2005). "Decay of cultivated apricot wood (Prunus armeniaca) by the ascomycete Hypocrea sulphurea, using solid state 13C NMR and off-line TMAH thermochemolysis with GC–MS." International Biodeterioration & Biodegradation 55(3): 175-185.
  5. a b Stamets, Paul (2005). Mycelium running: how mushrooms can help save the world. Random House, Inc. pp. 83–84. ISBN 978-1-58008-579-3.
  6. a b Vane, C. H., et al. (2001). "The effect of fungal decay (Agaricus bisporus) on wheat straw lignin using pyrolysis–GC–MS in the presence of tetramethylammonium hydroxide (TMAH)." Journal of Analytical and Applied Pyrolysis 60(1): 69-78.
  7. a b Vane, C. H., et al. (2006). "Bark decay by the white-rot fungus Lentinula edodes: Polysaccharide loss, lignin resistance and the unmasking of suberin." International Biodeterioration & Biodegradation 57(1): 14-23.
  8. ^ http://www.ipm.ucdavis.edu/PMG/PESTNOTES/pn74109.html.
  9. a b Cohen, R.; Persky, L.; Hadar, Y. (2002). "Biotechnological applications and potential of wood-degrading mushrooms of the genus Pleurotus(PDF)Applied Microbiology and Biotechnology 58 (5): 582–94. doi:10.1007/s00253-002-0930-. PMID 11956739.
  10. ^ Vane, C. H., et al. (2003). "Biodegradation of Oak (Quercus alba) Wood during Growth of the Shiitake Mushroom (Lentinula edodes):  A Molecular Approach." Journal of Agricultural and Food Chemistry 51(4): 947-956.
Further Reading

  • Schwarze, Francis W. M. R.; Engels, Julia; Mattheck, Claus (2000). Fungal Strategies of Wood Decay in Trees. Springer. ISBN 978-3-540-67205-0.
  • Mycorrhizal fungi and soil carbon storage
  • White, Robert H.; Ross, Robert J. (November 2014). Wood and Timber Condition Assessment Manual (2nd ed.). Madison, WI: United States Department of Agriculture, Forest Service, Forest Products Laboratory. Retrieved 31 January 2015.
  • Wasser, Zmitrovich I. V.; Engels, Tura (2014). Wood-inhabiting fungi (PDF). Fungi from different substrates / J. K. Misra, J. P. Tewari, S. K. Deshmukh, C. Vágvölgyi (eds). N. Y.: CRC Press, Taylor and Francis group.

- Wikipedia 

BIODEGRADATION

Biodegradation is the chemical dissolution of materials by bacteria, fungi. Although often conflated, biodegradable is distinct in meaning from compostable. While biodegradable simply means to be consumed by microorganisms, "compostable" makes the specific demand that the object break down under composting conditions. The term is often used in relation to ecology, waste management, biomedicine, and the natural environment (bioremediation) and is now commonly associated with environmentally friendly products that are capable of decomposing back into natural elements. Organic material can be degraded aerobically with oxygen or anaerobically, without oxygen. Biosurfactant, an extracellular surfactant secreted by microorganisms, enhances the biodegradation process.


Yellow slime mold growing on a bin of wet paper

Biodegradable matter is generally organic material that serves as a nutrient for microorganisms. Microorganisms are so numerous and diverse that, a huge range of compounds are biodegraded, including hydrocarbons (e.g. oil), polychlorinated biphenyls (PCBs), polyaromatic hydrocarbons (PAHs), pharmaceutical substances. Decomposition of biodegradable substances may include both biological and abiotic steps.

IUPAC definition
" Degradation caused by enzymatic process resulting from the action of cells.
Note: Modified to exclude abiotic enzymatic processes".

Factors affecting rate

In practice, almost all chemical compounds and materials are subject to biodegradation, the key is the relative rates of such processes - minutes, days, years, centuries... A number of factors determine the degradation rate of organic compounds. Salient factors include light, water and oxygen. Temperature is also important because chemical reactions proceed more quickly at higher temperatures. The degradation rate of many organic compounds is limited by their bioavailability. Compounds must be released into solution before organisms can degrade them.
Biodegradability can be measured in a number of ways. Respirometry tests can be used for aerobic microbes. First one places a solid waste sample in a container with microorganisms and soil, and then aerate the mixture. Over the course of several days, microorganisms digest the sample bit by bit and produce carbon dioxide – the resulting amount of CO2serves as an indicator of degradation. Biodegradability can also be measured by anaerobic microbes and the amount of methane or alloy that they are able to produce. In formal scientific literature, the process is termed bio-remediation.
Approximated time for compounds to biodegrade in a marine environment
ProductTime to Biodegrade
Paper towel2–4 weeks
Newspaper6 weeks
Apple core2 months
Cardboard box2 months
Wax coated milk carton3 months
Cotton gloves1–5 months
Wool gloves1 year
Plywood1–3 years
Painted wooden sticks13 years
Plastic bags10–20 years
Tin cans50 years
Disposable diapers50–100 years
Plastic bottle100 years
Aluminium cans200 years
Glass bottlesUndetermined
Detergents

In advanced societies, laundry detergents are based on linear alkylbenzenesulfonates. Branched alkybenzenesulfonates (below right), used in former times, were abandoned because they biodegrade too slowly.

Plastics

Plastics biodegrade at highly variable rates. PVC- based plumbing is specifically selected for handing sewage because PVC biodegrades very slowly. Some packaging materials on the other hand are being developed that would degrade readily upon exposure to the environment. Illustrative synthetic polymers that are biodegrade quickly include polycaprolactone, others are polyesters and aromatic-aliphatic esters, due to their ester bonds being susceptible to attack by water. A prominent example is poly-3-hydroxybutyrate, the renewably derived polylactic acid, and the synthetic polycaprolactone. Others are the cellulose-based cellulose acetate and celluloid (cellulose nitrate).
Under low oxygen conditions biodegradable plastics break down slower and with the production of methane, like other organic materials do. The breakdown process is accelerated in a dedicated compost heap. Starch-based plastics will degrade within two to four months in a home compost bin, while polylactic acid is largely undecomposed, requiring higher temperatures. Polycaprolactone and polycaprolactone-starch composites decompose slower, but the starch content accelerates decomposition by leaving behind a porous, high surface area polycaprolactone. Nevertheless, it takes many months. In 2016, a bacterium named Ideonella sakaiensis was found to biodegrade PET.
Polylactic acid is an example of a plastic that biodegrades quickly.
Many plastic producers have gone so far even to say that their plastics are compostable, typically listing corn starch as an ingredient. However, these claims are questionable because the plastics industry operates under its own definition of compostable:
"that which is capable of undergoing biological decomposition in a compost site such that the material is not visually distinguishable and breaks down into carbon dioxide, water, inorganic compounds and biomass at a rate consistent with known compostable materials." (Ref: ASTM D 6002)
The term "composting" is often used informally to describe the biodegradation of packaging materials. Legal definitions exist for compostability, the process that leads to compost. Four criteria are offered by the European Union:
  • Biodegradability, the conversion of >90% material material into CO2 and water by the action of micro-organisms within 6 months.
  • Disintegrability, the fragmentation of 90% of the original mass to particles that then pass through a 2 mm sieve.
  • Absence of toxic substances and other substances that impede composting.

Biodegradable technology
In 1973 it was proven for the first time that polyester degrades when disposed in bioactive material such as soil. Polyesters are water resistant and can be melted and shaped into sheets, bottles, and other products, making certain plastics now available as a biodegradable product. Following, Polyhydroxylalkanoates (PHAs) were produced directly from renewable resources by microbes. They are approximately 95% cellular bacteria and can be manipulated by genetic strategies. The composition and biodegradability of PHAs can be regulated by blending it with other natural polymers. In the 1980s the company ICI Zenecca commercialized PHAs under the name Biopol. It was used for the production of shampoo bottles and other cosmetic products. Consumer response was unusual. Consumers were willing to pay more for this product because it was natural and biodegradable, which had not occurred before.
Now biodegradable technology is a highly developed market with applications in product packaging, production and medicine. Biodegradable technology is concerned with the manufacturing science of biodegradable materials. It imposes science based mechanisms of plant genetics into the processes of today. Scientists and manufacturing corporations can help impact climate change by developing a use of plant genetics that would mimic some technologies. By looking to plants, such as biodegradable material harvested through photosynthesis, waste and toxins can be minimized.
Oxo-biodegradable technology, which has further developed biodegradable plastics, has also emerged. Oxo-biodegradation is defined by CEN (the European Standards Organisation) as "degradation resulting from oxidative and cell-mediated phenomena, either simultaneously or successively." Whilst sometimes described as "oxo-fragmentable," and "oxo-degradable" this describes only the first or oxidative phase. These descriptions should not be used for material which degrades by the process of oxo-biodegradation defined by CEN, and the correct description is "oxo-biodegradable."
By combining plastic products with very large polymer molecules, which contain only carbon and hydrogen, with oxygen in the air, the product is rendered capable of decomposing in anywhere from a week to one to two years. This reaction occurs even without prodegradant additives but at a very slow rate. That is why conventional plastics, when discarded, persist for a long time in the environment. Oxo-biodegradable formulations catalyze and accelerate the biodegradation process but it takes considerable skill and experience to balance the ingredients within the formulations so as to provide the product with a useful life for a set period, followed by degradation and biodegradation.
Biodegradable technology is especially utilized by the bio-medical community. Biodegradable polymers are classified into three groups: medical, ecological, and dual application, while in terms of origin they are divided into two groups: natural and synthetic. The Clean Technology Group is exploiting the use of supercritical carbon dioxide, which under high pressure at room temperature is a solvent that can use biodegradable plastics to make polymer drug coatings. The polymer (meaning a material composed of molecules with repeating structural units that form a long chain) is used to encapsulate a drug prior to injection in the body and is based on lactic acid, a compound normally produced in the body, and is thus able to be excreted naturally. The coating is designed for controlled release over a period of time, reducing the number of injections required and maximizing the therapeutic benefit. Professor Steve Howdle states that biodegradable polymers are particularly attractive for use in drug delivery, as once introduced into the body they require no retrieval or further manipulation and are degraded into soluble, non-toxic by-products. Different polymers degrade at different rates within the body and therefore polymer selection can be tailored to achieve desired release rates.
Other biomedical applications include the use of biodegradable, elastic shape-memory polymers. Biodegradable implant materials can now be used for minimally invasive surgical procedures through degradable thermoplastic polymers. These polymers are now able to change their shape with increase of temperature, causing shape memory capabilities as well as easily degradable sutures. As a result, implants can now fit through small incisions, doctors can easily perform complex deformations, and sutures and other material aides can naturally biodegrade after a completed surgery.
Etymology of "biodegradable"

The first known use of the word in biological text was in 1961 when employed to describe the breakdown of material into the base components of carbon, hydrogen, and oxygen by microorganisms. Now biodegradable is commonly associated with environmentally friendly products that are part of the earth's innate cycle and capable of decomposing back into natural elements.

References

  1. ^ "Terminology for biorelated polymers and applications (IUPAC Recommendations 2012)" (PDF)Pure and Applied Chemistry 84 (2): 377–410. 2012. doi:10.1351/PAC-REC-10-12-04.
  2. ^ Sims, G. K. and A.M. Cupples. 1999. Factors controlling degradation of pesticides in soil. Pesticide Science 55:598–601.
  3. ^ Sims, G.K. (1991). The effects of sorption on the bioavailability of pesticides. London: Springer Verlag. pp. 119–137.
  4. ^ "Measuring Biodegradability, The University of Waikato, June 19, 2008
  5. ^ "Marine Debris Biodegradation Time Line", C-MORE, citing Mote Marine Laboratory,1993.
  6. ^ Kurt Kosswig,"Surfactants" in Ullmann's Encyclopedia of Industrial Chemistry, Wiley-VCH, 2005, Weinheim. doi:10.1002/14356007.a25_747.
  7. ^ Kyrikou, Ioanna; Briassoulis, Demetres (12 Apr 2007). "Biodegradation of Agricultural Plastic Films: A Critical Review". Journal of Polymers and the Environment (SpringerLink) 15 (2): 125–150. doi:10.1007/s10924-007-0053-8. Retrieved 30 May 2015.
  8. ^ "Microsoft Word - SECTION 6 BIODEGRADABILITY OF PACKAGING WASTE.doc (PDF). Www3.imperial.ac.uk. Retrieved 2014-03-02.
  9. ^ Fig.9.
  10. ^ "Compostable.info".Compostable.info. Retrieved 2014-03-02.
  11. ^ http://greenplastics.com/wiki/EN_13432.
  12. ^ M. Breulmann et al. "Polymers, Biodegradable" in Ullmann's Encyclopedia of Industrial Chemistry 2012 Wiley-VCH, Weinheim.doi:10.1002/14356007.n21_n01.
  13. ^ Gross,Richard. "Biodegradable Polymers for the Environment", American Association of Advanced Science, August 2, 2002, p. 804.
  14. ^ Luzier, W. D. "Materials Derived from Biomass/Biodegradable Materials." Proceedings of the National Academy of Sciences 89.3 (1992): 839–42. Print.
  15. ^ Agamuthu, P."Biodegradability and Degradability of Plastic Waste, "International Solid Waste Association" November 9, 2004
Standard by ASTM International

  • D5210- Standard Test Method for Determining the Anaerobic Biodegradation of Plastic Materials in the Presence of Municipal Sewage Sludge
  • D5526- Standard Test Method for Determining Anaerobic Biodegradation of Plastic Materials Under Accelerated Landfill Conditions
  • D5338- Standard Test Method for Determining Aerobic Biodegradation of Plastic Materials Under Controlled Composting Conditions, Incorporating Thermophilic Temperatures
  • D5511- Standard Test Method for Determining Anaerobic Biodegradation of Plastic Materials Under High-Solids Anaerobic-Digestion Conditions
  • D5864- Standard Test Method for Determining Aerobic Aquatic Biodegradation of Lubricants or Their Components
  • D5988- Standard Test Method for Determining Aerobic Biodegradation of Plastic Materials in Soil
  • D6139- Standard Test Method for Determining the Aerobic Aquatic Biodegradation of Lubricants or Their Components Using the Gledhill Shake Flask
  • D6006- Standard Guide for Assessing Biodegradability of Hydraulic Fluids
  • D6340- Standard Test Methods for Determining Aerobic Biodegradation of Radiolabeled Plastic Materials in an Aqueous or Compost Environment
  • D6691- Standard Test Method for Determining Aerobic Biodegradation of Plastic Materials in the Marine Environment by a Defined Microbial Consortium or Natural Sea Water Inoculum
  • D6731-Standard Test Method for Determining the Aerobic, Aquatic Biodegradability of Lubricants or Lubricant Components in a Closed Respirometer
  • D6954- Standard Guide for Exposing and Testing Plastics that Degrade in the Environment by a Combination of Oxidation and Biodegradation
  • D7044- Standard Specification for Biodegradable Fire Resistant Hydraulic Fluids
  • D7373-Standard Test Method for Predicting Biodegradability of Lubricants Using a Bio-kinetic Model
  • D7475- Standard Test Method for Determining the Aerobic Degradation and Anaerobic Biodegradation of Plastic Materials under Accelerated Bioreactor Landfill Conditions
  • D7665- Standard Guide for Evaluation of Biodegradable Heat Transfer Fluids

External Links



- Wikipedia 

Advantages and Disadvantages of Fasting for Runners

Author BY   ANDREA CESPEDES  Food is fuel, especially for serious runners who need a lot of energy. It may seem counterintuiti...