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Aquatic crops

Aquatic crops. A wide variety of aquatic biomass resources exist, such as algae, giant kelp, other seaweed, and marine microflora. Commercial examples include giant kelp extracts for thickeners and food additives, algal dyes, and novel biocatalysts for use in bioprocessing under extreme environments. [Pg.122]

Energy crops Herbaceous, woody, industrial, agricultural and aquatic crops (seaweed and... [Pg.269]

A number of different types of domestic biomass resources (also referred to as feedstocks) are used to produce bioenergy. These include biomass processing residues such as paper and pulp, agricultural and forestry wastes, urban landfill waste and gas, animal (including human) sewage and manure waste, and land and aquatic crops. There are basically two... [Pg.186]

Energy crops Herbaceous energy crops, woody energy crops, industrial crops, agricultural crops, and aquatic crops... [Pg.352]

Bipyridiniums. The bipyridinium herbicides (Table 2), paraquat and diquat, ate nonselective contact herbicides and crop desiccants. Diquat is also used as a general aquatic herbicide (2,296). Bipyridinium herbicides are organic cations and are retained ia the soil complex via cation exchange. They are strongly sorbed to most soils and are not readily desorbed (332). Both paraquat and diquat are not readily leached (293). [Pg.50]

Linear alkylbenzenesulfonate showed no deleterious effect on agricultural crops exposed to this material (54,55). Kinetics of biodegradation have been studied in both wastewater treatment systems and natural degradation systems (48,57,58). Studies have concluded that linear alkylbenzenesulfonate does not pose a risk to the environment (50). Linear alkylbenzenesulfonate has a half-life of approximately one day in sewage sludge and natural water sources and a half-life of one to three weeks in soils. Aquatic environmental safety assessment has also shown that the material does not pose a hazard to the aquatic environment (56). [Pg.99]

Until recently, the NRA has not participated during the approval process in assessing the potential environmental impact of pesticides. However, the NRA does supply monitoring data to MAFF and HSE for pesticide reviews. These occur once a pesticide has been approved for use for a certain length of time, or when further information is needed on an approved pesticide. In supplying these data, the NRA comments on any areas of concern. This contributed to the 1993 ban on the use of atrazine and simazine on non-cropped land. In January 1995 the NRA s National Centre for Toxic and Persistent Substances (TAPS) was made advisor to the DoF, on the potential impact on the aquatic environment of... [Pg.55]

Methyl parathion has been released to the environment mainly as a result of its use as an insecticide on crops. It is applied to agricultural crops by aerial or ground spraying equipment. Methyl parathion has been detected in surface waters and sediments, rainwater, aquatic organisms, and food. There are no known natural sources of the compound. Methyl parathion has been identified in at least 16 of the 1,585 hazardous waste sites on the NPL (HazDat 2001). [Pg.147]

Seeds of lettuce and other species have frequently been used to bioassay for the allelopathic activity of plant exudates (17.18.19). As with the use of cell suspensions, there are certain advantages and disadvantages to this methodology. The experimental simplicity, small amounts of material required and short time frame are certainly attractive qualities. However, species used in such bioassays quite often do not represent the actual target species under consideration. This is especially true when terrestrial crop species are substituted for weeds of aquatic systems. Nevertheless, information obtained from such experiments are often valuable when used in conjunction with results of other assays. [Pg.410]

Contamination of aquatic foodstuffs by the radiocerium in fallout from weapons tests and effluents from nuclear power facilities is well documented. The concentrations of 144Ce in clam muscle and cuttlefish in Japan in 1960 exceeded those of Sr by one to two orders of magnitude and were somewhat greater than those measured in food crops (Nezu et al., 1962). Radiocerium was detected in only a few samples of aquatic foods monitored in the Central Pacific during nuclear device testing there in 1962 (Welander and Palumbo, 1963 ... [Pg.18]

Proposed copper criteria for the protection of agricultural crops, aquatic life, terrestrial invertebrates, poultry, laboratory white rats, livestock, and human health are summarized in Table 3.8. [Pg.207]

Copper discharges to the global biosphere are due primarily to human activities, especially mining, smelting, and refining copper and the treatment and recycling of municipal and industrial wastes. Some copper compounds, especially copper sulfate, also contribute to environmental copper burdens because they are widely and intensively used in confined geographic areas to control nuisance species of aquatic plants and invertebrates, diseases of terrestrial crop plants, and ectoparasites of fish and livestock. [Pg.213]

Data are scarce or missing on copper deficiency effects in aquatic flora and fauna and in avian and terrestrial mammalian wildlife additional studies of copper deficiency in these groups are merited. In sensitive terrestrial agricultural crops, copper deficiency occurs at less than 1.6 mg... [Pg.213]

Numerous and disparate copper criteria are proposed for protecting the health of agricultural crops, aquatic life, terrestrial invertebrates, poultry, laboratory white rats, and humans (Table 3.8) however, no copper criteria are now available for protection of avian and mammalian wildlife, and this needs to be rectified. Several of the proposed criteria do not adequately protect sensitive species of plants and animals and need to be reexamined. Other research areas that merit additional effort include biomarkers of early copper stress copper interactions with interrelated trace elements in cases of deficiency and excess copper status effects on disease resistance, cancer, mutagenicity, and birth defects mechanisms of copper tolerance or acclimatization and chemical speciation of copper, including measurement of flux rates of ionic copper from metallic copper. [Pg.215]

AGRICULTURAL CROPS Irrigation water, tolerated level AQUATIC LIFE Freshwater organisms Sensitive species, tolerated level <15,000 pg/L 1... [Pg.768]


See other pages where Aquatic crops is mentioned: [Pg.184]    [Pg.22]    [Pg.483]    [Pg.1]    [Pg.184]    [Pg.22]    [Pg.483]    [Pg.1]    [Pg.468]    [Pg.31]    [Pg.43]    [Pg.45]    [Pg.253]    [Pg.142]    [Pg.105]    [Pg.185]    [Pg.131]    [Pg.157]    [Pg.188]    [Pg.310]    [Pg.48]    [Pg.121]    [Pg.35]    [Pg.39]    [Pg.1161]    [Pg.141]    [Pg.1]    [Pg.12]    [Pg.250]    [Pg.182]    [Pg.69]    [Pg.264]    [Pg.371]    [Pg.68]    [Pg.583]    [Pg.747]    [Pg.748]    [Pg.767]   
See also in sourсe #XX -- [ Pg.21 ]




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