Larva materials

Fibers (see Fibers, survey) used in textile production can have a wide variety of origins plants, ie, ceUulosic fibers (see Fibers, cellulose esters) animals, ie, protein fibers (see Wool) and, in the twentieth century, synthetic polymers. Depending on the part of the plant, the ceUulosic fibers can be classified as seed fibers, eg, cotton (qv), kapok bast fibers, eg, linen from flax, hemp, jute and leaf fibers, eg, agave. Protein fibers include wool and hair fibers from a large variety of mammals, eg, sheep, goats, camels, rabbits, etc, and the cocoon material of insect larvae (sUk). Real sUk is derived from the cocoon of the silkworm, Bombjx mori and for a long time was only produced in China, from which it was traded widely as a highly valuable material. 

Phenazine-l-carboxamide (137) is known as oxychlororaphine and has been isolated from cultures of Pseudomonas chlororaphisit has some limited inhibitory properties, but the inhibitory action of phenazines is generally disappointing. Some phenazine derivatives have insecticidal properties thus, phenazine itself has been found to be toxic to the clothes moth, the Hawaiian beet webworm, the rice weevil and larva of the codling moth, but under trial conditions its toxicity to plant material, as evidenced by severe burning of foliage, was found to be too high to make it of practical value. 

Worms - There are three types of worms found in water. For the most part, they dwell in the bed of the material at the bottom of lakes and streams. There they do important work as scavengers. The rotifiers are the only organisms in this category at or near the surfaee. They live primarily in stagnant fresh water. The eggs and larvae of various intestinal worms found in man and warm-blooded animals pollute the water at times. They do not generally cause widespread infection for several reasons. They are relatively few in number and are so large they can be filtered out of water with comparative ease. 

If flour or meal has become contaminated with storage insects after milling, the insect parts or larvae may be removed for identification by sieving or by a flotation procedure, but perhaps only excrement remains in the sample. This is about the same color as the material upon which the insects have fed and has generally the same appearance macroscopically. By means of the fluorescent light, however, pellets may be rendered more readily visible. If such flour is treated with clove oil, the pellets stand out distinctly and may be readily counted. 

Contamination by flies may occur directly in a factory, especially if material is allowed to stand unprotected for long periods while being held for processing. Failure to dispose of refuse promptly, particularly outside the plant, frequently creates ideal breeding and feeding places for these pests. Under such circumstances, parts of the adult vinegar fly, its larvae, or eggs, when found in the comminuted product, provide definite evidence of careless and insanitary operations. 

Bacillus thuringiensis produces a variety of organic compounds which are toxic to the larvae of certain susceptible insect hosts. Among the toxic entities are proteinaceous crystals, probably three soluble toxins, and certain enzymes. The protein material is the major toxin active in killing lepidopterous larvae. The protein is formed by the cells apparently in close synchrony with sporulation, and its nature is a constant function of bacterial strain. The mode of action of the protein is under study. The sequence of events in the pathology observed is probably solubilization of the crystal (enzymatic or physical)—>liberation of toxic unit—>alteration of permeability of larval gut wall— change in hemolymph pH—>invasion of hemolymph by spores or vegetative cells of the bacterium. 

Materials produced by crystalliferous bacilli which elicit a toxic response in susceptible insects may be separated into two types. The first type, the true toxins, include the crystalline protein inclusion body the parasporal body of Hannay (14)], a heat-stable, water-soluble exotoxin active against flies, a heat-stable, dialyzable water-soluble exotoxin, toxic to Lepidoptera on injection (23), and a heat-labile, water-soluble, filterable exotoxin, toxic toward larch sawfly larvae (Hymenoptera) which was reported by Smirnoff (31). 

Test dusts. 0.5% material + 0.05% pyreth Standard dust. 0.75% rotenone 10 larvae per test. Averages of 12 tests Dosage of dust. 0.283 gram per square foot... 

Because of the importance of safe insecticides in the protection of foods, additional tests have been run against German cockroaches, red flour beetles, and Mexican bean beetle larvae. The residual deposit test was used on the first two insects, and a dust test on the bean beetles. The procedure for the latter method is to incorporate the materials into dusts which are distributed on bean leaves (6) piperonyl cyclonene, which is superior to butoxide against this insect, was included in this series of tests. 

Biopsy material for schistosomiasis is better examined in teased preparations than in sections, as the entire thickness can be examined at once, and the viability of eggs can be determined by observation of the movement of the larvae within the eggs. 

Urine specimens usually are examined for the eggs of Schistosoma haemotobium or the trophozoites of Trichomonas vaginalis, although occasionally the larvae of Strongyloides stercoralis may be found in patients with hyperinfection syndrome. Urine is the usual specimen for the diagnosis of Trichomonas infection in males. See below (Vaginal Material) for culture method. Urine is centrifuged, and the sediment is examined microscopically. 

Sediments and biota collected from the Hersey River, Michigan, in 1978, were heavily contaminated with phenanthrene, benz[a]anthracene, and benzo[a]pyrene when compared to a control site. Elevated PAH concentrations were recorded in sediments, whole insect larvae, crayfish muscle, and flesh of lampreys (family Petromyzontidae), brown trout (Salmo trutta), and white suckers (Catostomus commersoni), in that general order (Black et al. 1981). The polluted collection locale was the former site of a creosote wood preservation facility between 1902 and 1949, and, at the time of the study, received Reed City wastewater treatment plant effluent, described as an oily material with a naphthalene-like odor (Black et al. 1981). In San Francisco Bay, elevated PAH concentrations in fish livers reflected elevated sediment PAH concentrations (Stehr et al. 1997). In Chesapeake Bay, spot (Leiostomus xanthurus) collected from a PAH-contaminated tributary (up to 96 mg PAHs/kg DW sediment) had elevated cytochrome P-450 and EROD activity in liver and intestine microsomes (Van Veld et al. 1990). Intestinal P-450 activity was 80 to 100 times higher in fish from highly contaminated sites than in conspecifics from reference sites intestinal EROD activity had a similar trend. Liver P-450 and EROD activity was about 8 times higher in spot from the contaminated sites when compared to the reference sites. Liver P-450 activity correlated positively with sediment PAH, but intestinal P-450 activity seemed to reflect dietary exposure (Van Veld et al. 1990). The poor correlation between hepatic concentrations of PAHs and P-4501A is attributed to the rapid metabolism of these compounds (van der Weiden et al. 1994). 

Many food raw materials and produets have to be treated with chemical insecticides to prevent losses due to damage eaused by fly larvae, beetles, and other inseets. This applies to, for example, dried fish, dried fruits, raisins, almonds, nuts, eoeoa beans, and grain. 

What to do Ensure that land is well-drained. When growing vegetables, use a strict crop rotation. Control woundforming pests like wireworms, slugs, and root-damaging larvae. Once rot has started, there is no cure. Dispose of or bury infected plant material. 

A number of lipid materials were shown to be toxic to the larvae of the bruchid beetle, Callosobruchus maculatus (96). 

Murray further explains that the inner surface of the larval trachea is composed of a waxy material, which is wetted by oil but not by water. According to Watson (55), the presence of any kind of oil in the tracheae is ultimately fatal. He shows, however, that survival time may vary from a few minutes to a week, depending on the toxicity and the amount of oil taken into the tracheal system. This amount varies with the number of times the larva contacts the oil film. 

In an effort to reduce costs, civic organizations have from time to time gathered waste crankcase oil for use in controlling mosquito larvae. Usually such mosquito control programs have failed, because waste crankcase oils are low in toxicity to mosquito larvae, they contain dirt and other materials that clog spray nozzles, and the collection and supply are imdependable. 

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