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1

Banerjee, Sudeshna. Trends in household coverage of modern infrastructure services in africa. [Washington, D.C: World Bank, 2009.

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2

Bauer, Steve. Aquatic habitat indicators and their application to water quality objectives within the Clean Water Act. Seattle, WA: United States Environmental Protection Agency, Region 10, 1999.

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3

Rabalais, Nancy N. An updated summary of status and trends in indicators of nutrient enrichment in the Gulf of Mexico. Stennis Space Center, MS: U.S. Environmental Protection Agency, Office of Water, Gulf of Mexico Program, 1993.

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4

Kashuba, Roxolana. Multilevel hierarchical modeling of benthic macroinvertebrate responses to urbanization in nine metropolitan regions across the conterminous United States. Reston, Va: U.S. Geological Survey, 2010.

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5

1952-, Ram Neil M., Calabrese Edward J. 1946-, and Christman R. F. 1936-, eds. Organic carcinogens in drinking water: Detection, treatment, and risk assessment. New York: Wiley, 1986.

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6

Peril in the ponds: Deformed frogs, politics, and a biologist's quest. Amherst: University of Massachusetts Press, 2012.

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7

Gottholm, Bernard W. Toxic contaminants in the Gulf of Maine. Rockville, Md: National Oceanic and Atmospheric Administration, National Ocean Service, Office of Ocean Resources Conservation and Assessment, 1992.

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8

Office, General Accounting. Superfund: Cleanups nearing completion indicate future challenges : report to the chairman, Subcommittee on Superfund, Recycling, and Solid Waste Management, Committee on Environment and Public Works, U.S. Senate. Washington, D.C: GAO, 1993.

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9

United States. Environmental Protection Agency. Office of Water., ed. Environmental indicators of water quality in the United States. Washington, D.C: U.S. Environmental Protection Agency, Office of Water, 1996.

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10

Malawi social indicators survey, 1995: A survey of the state of health, nutrition, water, sanitation, and education of children in Malawi. [Zomba]: Ministry of Economic Planning and Development, National Statistical Office and the Centre for Social Research, 1996.

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11

D, Tillman Fred, National Water Availability and Use Program., and Geological Survey (U.S.), eds. Methods and indicators for assessment of regional ground-water conditions in the southwestern United States. Reston, Va: U.S. Geological Survey, 2008.

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12

D, Tillman Fred, National Water Availability and Use Program., and Geological Survey (U.S.), eds. Methods and indicators for assessment of regional ground-water conditions in the southwestern United States. Reston, Va: U.S. Geological Survey, 2008.

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13

D, Tillman Fred, National Water Availability and Use Program., and Geological Survey (U.S.), eds. Methods and indicators for assessment of regional ground-water conditions in the southwestern United States. Reston, Va: U.S. Geological Survey, 2008.

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14

D, Tillman Fred, National Water Availability and Use Program., and Geological Survey (U.S.), eds. Methods and indicators for assessment of regional ground-water conditions in the southwestern United States. Reston, Va: U.S. Geological Survey, 2008.

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15

Negus Cleary, Michelle. Social Complexity and Political Capitals in Ancient Eurasia. Oxford University Press, 2018. http://dx.doi.org/10.1093/oxfordhb/9780199935413.013.19.

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This article draws upon archaeological evidence of settlement and enclosure sites as key indicators of social complexity in agro-pastoral societies of Central Asia and Inner Eurasia during the Late Iron Age–Late Antique periods. Large fortified enclosures (kalas) were the political capitals of mobile states and empires, embodying and displaying the power, status, and prestige of ruling elites. Low-density “urban” sites were located in dispersed settlement zones associated with rivers or water management systems in the Eurasian steppe and oases. These capitals were an alternative form of urbanism suited to the political organization of mobile ruling elites. This analysis provides insights into the varied modes of settlement utilized by agro-pastoral and mobile societies in extreme environmental zones.
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16

Central African Republic. Bureau central du recensement., ed. Enquête à indicateurs multiples MICS-RCA 1996 sur la santé, l'éducation, l'eau et l'assainissement: Rapport final. [Bangui]: République Centrafricaine, Ministère de la réforme économique, du plan et de la coopération internationale, Division des statistiques et des études économiques, Bureau central du recensement, 1997.

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17

Gulf of Mexico Program (U.S.). Nutrient Enrichment Subcommittee., ed. An updated summary of status and trends in indicators of nutrient enrichment in the Gulf of Mexico. Stennis Space Center, MS: U.S. Environmental Protection Agency, Office of Water, Gulf of Mexico Program, 1993.

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18

Gulf of Mexico Program (U.S.). Nutrient Enrichment Subcommittee, ed. An updated summary of status and trends in indicators of nutrient enrichment in the Gulf of Mexico. Stennis Space Center, MS: U.S. Environmental Protection Agency, Office of Water, Gulf of Mexico Program, 1993.

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19

Impacts on quality of inland wetlands of the United States: A survey of indicators, techniques, and applications of community-level biomonitoring data. Corvallis, Or: USEPA Environmental Research Laboratory, 1990.

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20

H, Brandt Karla, and Corvallis Environmental Research Laboratory, eds. Impacts on quality of inland wetlands of the United States: A survey of indicators, techniques, and applications of community-level biomonitoring data. Corvallis, Or: USEPA Environmental Research Laboratory, 1990.

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21

H, Brandt Karla, and Corvallis Environmental Research Laboratory, eds. Impacts on quality of inland wetlands of the United States: A survey of indicators, techniques, and applications of community-level biomonitoring data. Corvallis, Or: USEPA Environmental Research Laboratory, 1990.

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22

Ellen, Hinck Jo, Biomonitoring of Environmental Status and Trends Program (Geological Survey), and Geological Survey (U.S.), eds. Biomonitoring of Environmental Status and Trends (BEST) Program: Environmental contaminants, health indicators, and reproductive biomarkers in fish from the Mobile, Apalachicola-Chattahoochee-Flint, Savannah, and Pee Dee River basins. Reston, Va: U.S. Geological Survey, 2007.

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23

Martin, Jeffrey J. Positive Affect. Oxford University Press, 2017. http://dx.doi.org/10.1093/oso/9780190638054.003.0022.

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This chapter examines disability sport research on positive affect that ranges from momentary emotions to broader and longer-lasting affective states. The chapter is organized in three ways: a hedonic perspective of momentary experiences of pleasure, engagement such as the experience of flow in sport and peak experiences in hiking and mountain climbing, and obtaining meaning in life, such as contributing to the broader society. Research in these three categories is presented. A plethora of research in disability sport has indicated that sport participation is associated with life satisfaction. Other researchers examining disabled military veterans have shown evidence of posttraumatic growth after acquisition of a disability and have shown how sport has helped facilitate such growth. Research on noncompetitive sport has also indicated that feelings of gratitude and well-being are associated with activities such as hiking, mountain climbing, and water-based activities. The chapter concludes with advocacy for an examination of flow in disability sport.
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24

Smith, Zach. Lyme Disease. Oxford University Press, 2016. http://dx.doi.org/10.1093/med/9780199976805.003.0050.

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Lyme disease (LD) is a tick-borne illness caused by Borrelia burgdorferi that causes a range of symptoms, including rash, constitutional symptoms, arthritis, and neurologic or cardiac abnormalities. LD presents in three stages: primary, early disseminated, and tertiary disseminated. Each stage is highly variable in onset and presentation, and symptoms may manifest across multiple stages. Patients with early stages of LD are often seronegative, so the decision to treat is clinical. A history of a tick bite plus EM is a clear indication for antibiotics; early antibiotics may reduce the severity and duration of symptoms. A vaccine is not available at this time, and LD is not transmitted through people, food, water, or blood; however, B. Burgdorferi has been identified living in stored donated blood. If acquired during pregnancy, LD can be transmitted through the placenta to the fetus; after treatment, no known harm to the fetus has been identified.
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25

Kirchman, David L. The nitrogen cycle. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198789406.003.0012.

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Nitrogen is required for the biosynthesis of many cellular components and can take on many oxidation states, ranging from −3 to +5. Consequently, nitrogen compounds can act as either electron donors (chemolithotrophy) or electron acceptors (anaerobic respiration). The nitrogen cycle starts with nitrogen fixation, the reduction of nitrogen gas to ammonium. Nitrogen fixation is carried out only by prokaryotes, mainly some cyanobacteria and heterotrophic bacteria. The ammonium resulting from nitrogen fixation is quickly used by many organisms for biosynthesis, being preferred over nitrate as a nitrogen source. It is also oxidized aerobically by chemolithoautotrophic bacteria and archaea during the first step of nitrification. The second step, nitrite oxidation, is carried out by other bacteria not involved in ammonia oxidation, resulting in the formation of nitrate. Some bacteria are capable of carrying out both steps (“comammox”). This nitrate can then be reduced to nitrogen gas or nitrous oxide during denitrification. It can be reduced to ammonium, a process called “dissimilatory nitrate reduction to ammonium.” Nitrogen gas is also released by anaerobic oxidation of ammonium (“anammox”) which is carried out by bacteria in the Planctomycetes phylum. The theoretical contribution of anammox to total nitrogen gas release is 29%, but the actual contribution varies greatly. Another gas in the nitrogen cycle, nitrous oxide, is a greenhouse gas produced by ammonia-oxidizing bacteria and archaea. The available data indicate that the global nitrogen cycle is in balance, with losses from nitrogen gas production equaling gains via nitrogen fixation. But excess nitrogen from fertilizers is contributing to local imbalances and several environmental problems in drinking waters, reservoirs, lakes, and coastal oceans.
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26

Vuorinen, Ilppo. Post-Glacial Baltic Sea Ecosystems. Oxford University Press, 2018. http://dx.doi.org/10.1093/acrefore/9780190228620.013.675.

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Post-glacial aquatic ecosystems in Eurasia and North America, such as the Baltic Sea, evolved in the freshwater, brackish, and marine environments that fringed the melting glaciers. Warming of the climate initiated sea level and land rise and subsequent changes in aquatic ecosystems. Seminal ideas on ancient developing ecosystems were based on findings in Swedish large lakes of species that had arrived there from adjacent glacial freshwater or marine environments and established populations which have survived up to the present day. An ecosystem of the first freshwater stage, the Baltic Ice Lake initially consisted of ice-associated biota. Subsequent aquatic environments, the Yoldia Sea, the Ancylus Lake, the Litorina Sea, and the Mya Sea, are all named after mollusc trace fossils. These often convey information on the geologic period in question and indicate some physical and chemical characteristics of their environment. The ecosystems of various Baltic Sea stages are regulated primarily by temperature and freshwater runoff (which affects directly and indirectly both salinity and nutrient concentrations). Key ecological environmental factors, such as temperature, salinity, and nutrient levels, not only change seasonally but are also subject to long-term changes (due to astronomical factors) and shorter disturbances, for example, a warm period that essentially formed the Yoldia Sea, and more recently the “Little Ice Age” (which terminated the Viking settlement in Iceland).There is no direct way to study the post-Holocene Baltic Sea stages, but findings in geological samples of ecological keystone species (which may form a physical environment for other species to dwell in and/or largely determine the function of an ecosystem) can indicate ancient large-scale ecosystem features and changes. Such changes have included, for example, development of an initially turbid glacial meltwater to clearer water with increasing primary production (enhanced also by warmer temperatures), eventually leading to self-shading and other consequences of anthropogenic eutrophication (nutrient-rich conditions). Furthermore, the development in the last century from oligotrophic (nutrient-poor) to eutrophic conditions also included shifts between the grazing chain (which include large predators, e.g., piscivorous fish, mammals, and birds at the top of the food chain) and the microbial loop (filtering top predators such as jellyfish). Another large-scale change has been a succession from low (freshwater glacier lake) biodiversity to increased (brackish and marine) biodiversity. The present-day Baltic Sea ecosystem is a direct descendant of the more marine Litorina Sea, which marks the beginning of the transition from a primeval ecosystem to one regulated by humans. The recent Baltic Sea is characterized by high concentrations of pollutants and nutrients, a shift from perennial to annual macrophytes (and more rapid nutrient cycling), and an increasing rate of invasion by non-native species. Thus, an increasing pace of anthropogenic ecological change has been a prominent trend in the Baltic Sea ecosystem since the Ancylus Lake.Future development is in the first place dependent on regional factors, such as salinity, which is regulated by sea and land level changes and the climate, and runoff, which controls both salinity and the leaching of nutrients to the sea. However, uncertainties abound, for example the future development of the Gulf Stream and its associated westerly winds, which support the sub-boreal ecosystems, both terrestrial and aquatic, in the Baltic Sea area. Thus, extensive sophisticated, cross-disciplinary modeling is needed to foresee whether the Baltic Sea will develop toward a freshwater or marine ecosystem, set in a sub-boreal, boreal, or arctic climate.
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27

Voinescu, Alexandra, Nadia Wasi Iqbal, and Kevin J. Martin. Management of chronic kidney disease-mineral and bone disorder. Edited by David J. Goldsmith. Oxford University Press, 2018. http://dx.doi.org/10.1093/med/9780199592548.003.0118_update_001.

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In all patients with chronic kidney disease (CKD) stages 3–5, regular monitoring of serum markers of CKD-mineral and bone disorder, including calcium (Ca), phosphorus (P), parathyroid hormone (PTH), 25-hydroxyvitamin D, and alkaline phosphatase, is recommended. Target ranges for these markers are endorsed by guidelines. The principles of therapy for secondary hyperparathyroidism include control of hyperphosphataemia, correction of hypocalcaemia, use of vitamin D sterols, use of calcimimetics, and parathyroidectomy. of hyperphosphataemia is crucial and may be achieved by means of dietary P restriction, use of P binders, and P removal by dialysis. Dietary P restriction requires caution, as it may be associated with protein malnutrition. Aluminium salts are effective P binders, but they are not recommended for long-term use, as Aluminium toxicity (though from contaminated dialysis water rather than oral intake) may cause cognitive impairment, osteomalacia, refractory microcytic anaemia, and myopathy. Ca-based P binders are also quite effective, but should be avoided in patients with hypercalcaemia, vascular calcifications, or persistently low PTH levels. Non-aluminium, non-Ca binders, like sevelamer and lanthanum carbonate, may be more adequate for such patients; however, they are expensive and may have several side effects. Furthermore, comparative trials have failed so far to provide conclusive evidence on the superiority of these newer P binders over Ca-based binders in terms of preventing vascular calcifications, bone abnormalities, and mortality. P removal is about 1800–2700 mg per week with conventional thrice-weekly haemodialysis, but may be increased by using haemodiafiltration or intensified regimens, such as short daily, extended daily or three times weekly nocturnal haemodialysis. Several vitamin D derivatives are currently used for the treatment of secondary hyperparathyroidism. In comparison with the natural form calcitriol, the vitamin D analogue paricalcitol seems to be more fast-acting and less prone to induce hypercalcaemia and hyperphosphataemia, but whether these advantages translate into better clinical outcomes is unknown. Calcimimetics such as cinacalcet can significantly reduce PTH, Ca, and P levels, but they have failed to definitively prove any benefits in terms of mortality and cardiovascular events in dialysis patients. Parathyroidectomy is often indicated in CKD patients with severe persistent hyperparathyroidism, refractory to aggressive medical treatment with vitamin D analogues and/or calcimimetics. This procedure usually leads to rapid improvements in biochemical markers (i.e. significant lowering of serum Ca, P, and PTH) and clinical manifestations (such as pruritus and bone pain); however, the long-term benefits are still unclear.
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28

Zydroń, Tymoteusz. Wpływ systemów korzeniowych wybranych gatunków drzew na przyrost wytrzymałości gruntu na ścinanie. Publishing House of the University of Agriculture in Krakow, 2019. http://dx.doi.org/10.15576/978-83-66602-46-5.

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The aim of the paper was to determine the influence of root systems of chosen tree species found in the Polish Flysch Carpathians on the increase of soil shear strength (root cohesion) in terms of slope stability. The paper's goal was achieved through comprehensive tests on root systems of eight relatively common in the Polish Flysch Carpathians tree species. The tests that were carried out included field work, laboratory work and analytical calculations. As part of the field work, the root area ratio (A IA) of the roots was determined using the method of profiling the walls of the trench at a distance of about 1.0 m from the tree trunk. The width of the. trenches was about 1.0 m, and their depth depended on the ground conditions and ranged from 0.6 to 1.0 m below the ground level. After preparing the walls of the trench, the profile was divided into vertical layers with a height of 0.1 m, within which root diameters were measured. Roots with diameters from 1 to 10 mm were taken into consideration in root area ratio calculations in accordance with the generally accepted methodology for this type of tests. These measurements were made in Biegnik (silver fir), Ropica Polska (silver birch, black locust) and Szymbark (silver birch, European beech, European hornbeam, silver fir, sycamore maple, Scots pine, European spruce) located near Gorlice (The Low Beskids) in areas with unplanned forest management. In case of each tested tree species the samples of roots were taken, transported to the laboratory and then saturated with water for at least one day. Before testing the samples were obtained from the water and stretched in a. tensile testing machine in order to determine their tensile strength and flexibility. In general, over 2200 root samples were tested. The results of tests on root area ratio of root systems and their tensile strength were used to determine the value of increase in shear strength of the soils, called root cohesion. To this purpose a classic Wu-Waldron calculation model was used as well as two types of bundle models, the so called static model (Fiber Bundle Model — FIRM, FBM2, FBM3) and the deformation model (Root Bundle Model— RBM1, RBM2, mRBM1) that differ in terms of the assumptions concerning the way the tensile force is distributed to the roots as well as the range of parameters taken into account during calculations. The stability analysis of 8 landslides in forest areas of Cicikowicleie and Wignickie Foothills was a form of verification of relevance of the obtained calculation results. The results of tests on root area ratio in the profile showed that, as expected, the number of roots in the soil profile and their ApIA values are very variable. It was shown that the values of the root area ratio of the tested tree species with a diameter 1-10 ram are a maximum of 0.8% close to the surface of the ground and they decrease along with the depth reaching the values at least one order of magnitude lower than close to the surface at the depth 0.5-1.0 m below the ground level. Average values of the root area ratio within the soil profile were from 0.05 to 0.13% adequately for Scots pine and European beech. The measured values of the root area ratio are relatively low in relation to the values of this parameter given in literature, which is probably connected with great cohesiveness of the soils and the fact that there were a lot of rock fragments in the soil, where the tests were carried out. Calculation results of the Gale-Grigal function indicate that a distribution of roots in the soil profile is similar for the tested species, apart from the silver fir from Bie§nik and European hornbeam. Considering the number of roots, their distribution in the soil profile and the root area ratio it appears that — considering slope stability — the root systems of European beech and black locust are the most optimal, which coincides with tests results given in literature. The results of tensile strength tests showed that the roots of the tested tree species have different tensile strength. The roots of European beech and European hornbeam had high tensile strength, whereas the roots of conifers and silver birch in deciduous trees — low. The analysis of test results also showed that the roots of the studied tree species are characterized by high variability of mechanical properties. The values Of shear strength increase are mainly related to the number and size (diameter) of the roots in the soil profile as well as their tensile strength and pullout resistance, although they can also result from the used calculation method (calculation model). The tests showed that the distribution of roots in the soil and their tensile strength are characterized by large variability, which allows the conclusion that using typical geotechnical calculations, which take into consideration the role of root systems is exposed to a high risk of overestimating their influence on the soil reinforcement. hence, while determining or assuming the increase in shear strength of soil reinforced with roots (root cohesion) for design calculations, a conservative (careful) approach that includes the most unfavourable values of this parameter should be used. Tests showed that the values of shear strength increase of the soil reinforced with roots calculated using Wu-Waldron model in extreme cases are three times higher than the values calculated using bundle models. In general, the most conservative calculation results of the shear strength increase were obtained using deformation bundle models: RBM2 (RBMw) or mRBM1. RBM2 model considers the variability of strength characteristics of soils described by Weibull survival function and in most cases gives the lowest values of the shear strength increase, which usually constitute 50% of the values of shear strength increase determined using classic Wu-Waldron model. Whereas the second model (mRBM1.) considers averaged values of roots strength parameters as well as the possibility that two main mechanism of destruction of a root bundle - rupture and pulling out - can occur at the same. time. The values of shear strength increase calculated using this model were the lowest in case of beech and hornbeam roots, which had high tensile strength. It indicates that in the surface part of the profile (down to 0.2 m below the ground level), primarily in case of deciduous trees, the main mechanism of failure of the root bundle will be pulling out. However, this model requires the knowledge of a much greater number of geometrical parameters of roots and geotechnical parameters of soil, and additionally it is very sensitive to input data. Therefore, it seems practical to use the RBM2 model to assess the influence of roots on the soil shear strength increase, and in order to obtain safe results of calculations in the surface part of the profile, the Weibull shape coefficient equal to 1.0 can be assumed. On the other hand, the Wu-Waldron model can be used for the initial assessment of the shear strength increase of soil reinforced with roots in the situation, where the deformation properties of the root system and its interaction with the soil are not considered, although the values of the shear strength increase calculated using this model should be corrected and reduced by half. Test results indicate that in terms of slope stability the root systems of beech and hornbeam have the most favourable properties - their maximum effect of soil reinforcement in the profile to the depth of 0.5 m does not usually exceed 30 kPa, and to the depth of 1 m - 20 kPa. The root systems of conifers have the least impact on the slope reinforcement, usually increasing the soil shear strength by less than 5 kPa. These values coincide to a large extent with the range of shear strength increase obtained from the direct shear test as well as results of stability analysis given in literature and carried out as part of this work. The analysis of the literature indicates that the methods of measuring tree's root systems as well as their interpretation are very different, which often limits the possibilities of comparing test results. This indicates the need to systematize this type of tests and for this purpose a root distribution model (RDM) can be used, which can be integrated with any deformation bundle model (RBM). A combination of these two calculation models allows the range of soil reinforcement around trees to be determined and this information might be used in practice, while planning bioengineering procedures in areas exposed to surface mass movements. The functionality of this solution can be increased by considering the dynamics of plant develop¬ment in the calculations. This, however, requires conducting this type of research in order to obtain more data.
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