Some Effects of Atmospheric Fluoride on Plant Metabolism

Leaves of Tendergreen bean plants exposed to atmospheric fluoride concentrations in the range 1.7 to 7.6 μg/m³ showed increased levels of enolase and catalase activity and decreased levels of pyruvate and α-ketoglutarate. Phosphoenolpyruvate carboxylase activity and oxalacetate were not affected. The leaves of Milo maize plants exposed to 5.0 μg F/m³ showed increased levels of enolase and pyruvate kinase activity and a decreased level of pyruvate. Oxalacetate and α-ketoglutarate levels were not affected. Catalase activity was increased, then decreased by IIF fumigation. The changes induced by HF were greatest six to 10 days after the start of fumigation and disappeared or decreased in magnitude during the post-fumigation period.     

Air Quality Standards for Fluoride Vegetation Effects

Facts that must be taken into consideration in developing fluoride standards for vegetation effects include: (1) Fluoride is an accumulative toxicant and injury is usually associated with long-term exposure; (2) gaseous and particulate fluorides differ in their phytotoxicity; (3) plant species and varieties differ greatly in susceptibility to fluoride; (4) extremely low concentrations can cause damage to sensitive species. Three possible approaches to standards are discussed: Atmospheric fluoride concentration, vegetation fluoride concentration, and the presence of leaf necrosis or chlorosis. Atmospheric fluoride concentration has the advantage that it fits the conventional concept of standards and that it is objective. Accurately measuring low fluoride concentrations, separating gaseous from particulate fluorides in the air sample, and establishing a safe concentration present technical problems, however. Vegetation analysis may more closely represent fluorides available to affect the plant. The presence of significant amounts of fluoride-induced leaf necrosis (e.g., 3% of the leaf area) may be the most practical approach to standards for fluoride vegetation effects. Advantages are that the combined effects of the forms of fluoride, species and varieties, and concentration-time relationships are all manifest in the factor that is measured. Relatively little time is required to examine the vegetation in a large area and only 2 or 3 surveys a year are required.     

Problems of Relating Atmospheric Analyses to Effects of Air Pollution on Agriculture

Relating of air pollution concentrations to effects on agriculture is hampered by deficiencies in present methods of atmospheric analysis and by inadequate knowledge about how various factors modify the effects. Analytical methods frequently lack sufficient sensitivity or specificity to determine accurately the substances involved. Typical examples include the difficulty of distinguishing among fluoride compounds with loidely differing phytotoxic activity, the serious interference from concomitant air pollutants with the usual methods of determining ozone, and the common failure or inability to detect short interval concentration extremes which may cause acute injury. The interrelationship of pollutant concentration and length of exposure in determining plant injury is poorly understood, as are the modifying effects of environmental conditions and age of tissue. The identity of some of the phytotoxic components of the urban photochemical pollution complex is still uncertain, making it difficult to select appropriate analytical methods. Caution should be exercised in using atmospheric analysis data to predict effects of air pollution on agriculture until these deficiencies in analytical methods and understanding of the problem are overcome.     

Fluoride effects on the mulberry-silkworm system

Absorption and accumulation of fluoride (F) from ambient air by mulberry leaves, and its transfer and effects on silkworm development, were examined. When the concentration of F in air exceeded 1.5 microg dm(-2). day (-1), using lime filter papers as static monitors, the F content of mulbery leaves was more than 30 ppm, the threshold for injury to silkworm larvae. Fluoride-polluted mulberry leaves inhibited growth and development of silkworms. Leaves containing more than 80 ppm F severely inhibited cocoon production. Fluoride was absorbed from the atmosphere by the mulberry leaf and was transferred to the silkworm, soil, water, and back to the atmosphere, forming a cycle.     

An Assessment of the Economic Effects of Ozone on U.S. Agriculture

Past attempts to measure the economic consequences of ozone on agriculture have been based on limited plant science information. This paper reports on an economic assessment of ozone on U.S. agriculture using recent crop response data from the National Crop Loss Assessment Network (NCLAN). The results are derived from a U.S. agricultural sector model that includes major crop and livestock production as well as domestic consumption, livestock feeding and export uses. The economic effects of four hypothetical ambient ozone levels are investigated. The analysis Indicates that the benefits to society of moderate (25%) ozone reductions are approximately $1.7 billion. A 25% Increase in ozone pollution results in costs (negative benefits) of $2.1 billion. These estimates do not reflect compliance costs of achieving the ozone changes and hence are not net benefits.     

A Reassessment of the Economic Effects of Ozone on U.S. Agriculture

The potential adverse effects of environmental change on agriculture have motivated considerable public research on this topic. Acid deposition, gaseous air pollutants, stratosphere ozone depletion and "green house" phenomena, individually and in combination, have been or are being evaluated in terms of effects on agricultural productivity. Assessments of the economic consequences of such effects have also been performed as input into the regulatory process. As with any applied bioeconomic analysis, the credibility of these economic assessments is dependent on the quality of the natural science and other data on the pollutant In question.

The ability of economists to assess the agricultural effects of one important pollutant, tropospheric ozone, has been Improved by the recently completed National Crop Loss Assessment Network (NCLAN). The structure, protocols and initial plant science findings of this U.S. Environmental Protection Agency program have been presented in this journal (see, for example, Heck et al).^1-2 In a related article,³ we reported the economic consequences of those preliminary ozone crop yield effects. Summary plant science findings have now been published.⁴

We provide here a more complete analysis of estimated benefits from reductions in troposphere ozone based on the final results of the NCLAN plant science research. In doing so, we concentrate on improvements in the modeling and underlying data which are reflected In this current assessment. While uncertainties still remain, these improvements should result in more defensible estimates of the magnitude of ozone’s effects on U.S. agriculture.     

The Microdetermination of Fluoride in Vegetation

This paper describes a micro method for the determination of the fluoride content of plant materials, particularly the leaves. The samples are dried and ground to a fine powder. Fifty milligram samples are burned in oxygen in 250-ml separatory funnels or in 300-ml Erienmeyer flasks. The gaseous products of the combustion are absorbed in 0.1 N NaOH in the closed funnel or flask and transferred to a small covered plastic dish in which the fluoride is diffused to tiny droplets of 3N sodium hydroxide solution distributed over the lower side of a tight fitting cover. The diffused fluoride is dissolved in water and determined colori-metrically by the SPADNS reagent.     

农业可持续发展的新模式：资源循环型农业

阐述了资源循环型农业的基本概念及其特征,根据循环经济的相关理论和国内外农业发展的实际情况,指出中国农业应在生态农业的基础上,朝着资源循环型农业的目标发展。     

Measurement of Ambient Ground-Level Concentrations of Hydrogen Fluoride

The use of published, accepted methods for measuring ambient levels of gaseous hydrogen fluoride (HF) with a double-tape sampler led to large errors. The major source of error was found to be scrubbing In the stainless steel intake, which was avoided by substituting Teflon for the stainless steel. To avoid this and other problems encountered in the measurement of HF, we revised the double-tape sampler method and modified the double-tape sampler. We designed and constructed an HF calibrator for use in testing the revised method and modified sampler In the field and laboratory.

The results of a round robin indicated that, in the laboratory, the revised method has a single-operator precision of 3 percent at 2.6 μg/m³ and a between-laboratory precision of 4 percent. The average bias at 2.6 μg/m³ was 0.02 μg/m³ and was not significantly different from zero. Comparable precision and accuracy were obtained in the field. The response was linear, at least to 10 μg/m³. The limit of detectability, which appears to be limited by the variability in measurements of blank tapes, is 0.07 μg/m³. The revised method appears both precise and accurate.     

Cytogenetic EffectsOf Hydrogen Fluoride TreatmentIn Tomato Plants

Seeds from tomato plants fumigated with hydrogen fluoride gas at a concentration of about 3 Mg/cu m were planted in pots in the greenhouse. A number of plants in each culture were found to be developing abnormally. These abnormalities consisted of one, three, or four cotyledons; deformed cotyledons; plumuless seedlings; fasciated petioles; wiry seedlings, double stalked plants; and dwarf seedlings. Such abnormal phenotypes were the same as, or similar to, known mutants. There was a trend toward a higher percentage of total phenotypic abnormalities with an increase in the treatment duration. Meiotic analyses of the Q. generation (offspring of the fumigated plants, Q) showed the occurrence of fragments or bridges plus fragments. There was also a trend toward a higher percentage of chromosomal aberrations with an increase in the treatment duration except for the 4 days duration which was higher than most of the other treatments. It is believed that the occurrence of these aberrations was due to crossing over in heterozygous paracentric inversions. These results suggest that HF is a mutagenic agent probably blocking directly or indirectly the replication of the DNA.     

Fluoride Cycling near A Coastal Emission Source

A strategy of research combining intense field monitoring and compartment modeling was used to characterize fluoride cycling in the semi-arid area around a newly installed aluminum factory in southern Argentina. The factory started operations In 1974 and emitted about 500 tons of gaseous fluorides to the atmosphere up to October 1976. Emphasis of research was on sedimentary or detritus cycling; periodically, samples were obtained from plant tissues, soils, sea water, and sea sediments. A compartment model of fluoride circulation at the atmosphere-vegetation interface provides further elements to Interpret the tendencies observed in field data. A fluoride budget up to October 1976 is presented showing the relative importance of environmental compartments monitored, with reference to fluoride accumulation. Plants are transient accumulators of atmospheric fluorides; soils, sea-water, and sea-sediments are sinks of the cycle. The major pathway of fluoride from terrestrial environment to coastal sea water Is along transportation with superficial soil eroded by wind. According to data here presented, it can be concluded that one wind storm can transport enough soluble fluorides to coastal waters to account for the transient differences of concentration observed.     

发展生态农业 实现农业循环经济

阐述了生态农业的基本理念和发展类型，提出了生态农业的发展策略。     

Fluoride loading of a lepidopteran larva (Pieris brassicae) fed on treated diets

Experiments to assess the impact of dietary fluoride on larvae of Pieris brassicae were designed to substantiate field observations that at polluted sites little fluoride is absorbed by insect larvae and that most of the body load is caused by surface contamination. Treatment with fluoride as HF or AlF3 had no effect on pupal weight of Pieris and we conclude that fluoride, at concentrations likely to be found on vegetation at polluted sites, is unlikely to have a direct impact on the growth of chewing herbivores. Fluoride in the gut formed the biggest component of the total body load. A significant amount of fluoride was detected in exuviae, but resulted from surface contamination. When larvae from polluted food were transferred to untreated food it took several days for the fluoride content of the faeces to return to background levels.     

离子选择电极法测定植物中的氟化物

离子选择电极法测定植物中的氟化物，植物样品先用0.05mol／L HNO3溶液浸提，然后再用0．1mol／L KOH溶液继续浸提，然后用氟离子选择性电极法来测定。     

Fluoride exposure decreased neurite formation on cerebral cortical neurons of SD rats in vitro

Environmental Science and Pollution Research - Fluoride, a geochemical element, can damage the brain and result in dysfunction of the central nervous system. In recent years, fluoride-induced...     

Fluoride accumulation and toxicity in wild small mammals

Populations of two species of small mammal, the field vole (Microtus agrestis L.) and the bank vole (Clethrionomys glareolus L.), inhabiting grasslands contaminated by industrial sources of fluoride were examined for fluoride concentrations in skeletal tissue and for morphological changes in the teeth. Concentrations of fluoride in teeth and bones were higher for C. glareolus than for M. agrestis at the chemical works and smelter sites. Severe dental lesions were recorded on the incisor and molar teeth of both species at the chemical works and smelter sites, with less marked damage at the mine tailings dam. This is attributed to inter-site differences in fluoride speciation and the consequent effects on the availability of fluoride in the diet for bioassimilation.     

Fluoride toxicity to aquatic organisms: a review

Published data on the toxicity of fluoride (F-) to algae, aquatic plants, invertebrates and fishes are reviewed. Aquatic organisms living in soft waters may be more adversely affected by fluoride pollution than those living in hard or seawaters because the bioavailability of fluoride ions is reduced with increasing water hardness. Fluoride can either inhibit or enhance the population growth of algae, depending upon fluoride concentration, exposure time and algal species. Aquatic plants seem to be effective in removing fluoride from contaminated water under laboratory and field conditions. In aquatic animals, fluoride tends to be accumulated in the exoskeleton of invertebrates and in the bone tissue of fishes. The toxic action of fluoride resides in the fact that fluoride ions act as enzymatic poisons, inhibiting enzyme activity and, ultimately, interrupting metabolic processes such as glycolysis and synthesis of proteins. Fluoride toxicity to aquatic invertebrates and fishes increases with increasing fluoride concentration, exposure time and water temperature, and decreases with increasing intraspecific body size and water content of calcium and chloride. Freshwater invertebrates and fishes, especially net-spinning caddisfly larvae and upstream-migrating adult salmons, appear to be more sensitive to fluoride toxicity than estuarine and marine animals. Because, in soft waters with low ionic content, a fluoride concentration as low as 0.5 mg F-/l can adversely affect invertebrates and fishes, safe levels below this fluoride/l concentration are recommended in order to protect freshwater animals from fluoride pollution.     

Evaluation of Probes Used for Source Sampling of Hydrogen Fluoride

The body of information presented in this paper is directed to those individuals concerned with methods for the sampling and measurement of fluorides contained in stack gases produced during the manufacture of phosphate fertilizer or aluminum. An air stream containing gaseous hydrogen fluoride (HF), at concentrations of from 87 to 1700 µg F m^-3, was generated and passed through 193 to 198 cm lengths of Pyrex glass, type 316 stainless steel, TFE Teflon, and methyl methacrylate-coated aluminum probes at flow rates of 28 I min^-1. HF passing through the probes was collected in deionized water contained in a Greenburg-Smith impinger. The Teflon probe exhibited no loss of HF and no trend toward increased passage of HF with time. Significant amounts of fluoride were lost in 18 out of 20 tests with the methacrylate probe and in 4 out of 20 tests with the Pyrex and stainless steel probes. Trends toward increased passage of HF with time occurred with the latter three probe materials. The selective ion electrode and semiautomated methods gave equivalent results when samples were made alkaline to avoid sorption of fluoride by Tygon tubing used in the semiautomated method. These results demonstrated that a Teflon probe gave the most representative sample of gaseous HF. However, additional tests are needed before a final recommendation is made for a probe to sample fluorides in stack gases.     

Further Evaluation of Glass Fiber Filters for Sampling Hydrogen Fluoride

Tests were conducted to determine the limitations of glass fiber filters in sampling atmospheric hydrogen fluoride. Filters without latex binder were more efficient collectors than those with the binder. Up to 75 μg F/in.² of filter area was collected by a single filter before the loss reached 5 percent. Two filters, one behind the other, collected over 250 μg F/in.² of filter area before loss through them reached five percent. By controlling the sampling rate and time to avoid exceeding the saturation limit, it is possible to use glass fiber filters for sampling over a wide range of fluoride concentrations.