The dust storms that blow over Iraq were studied from December 2008 to March 2009. The total number of studied dust storms was eight; during each dust storm, samples were collected from the cities of Baghdad, Ramadi, Kut, Basra, Najaf, Karbala, Hilla and Tikrit. The climatic elements with the dust storms types were studied. The results of dust storms analyses reflect their increase in average toward the southwestern direction (average suspended, rising, regional dust storms were 8, 10, 15 days/ year, respectively). The average means annual rainfall (in mm), evaporation (in mm), temperature (in°C), and relative humidity percentage indicate that there were remarkable variations in values, with increase of the number of days/ years of the dust storms reflecting the effect of the regional climatic change. The results of particle size analyses indicate the texture of most samples range from sandy clayey silt (75%) and clayey sandy silt (25%), and the average dominant grain size have a direct relationship with trajectories of dust storms. Quartz grains were 15% rounded and 85% sub-rounded. Moreover, the dust samples were analyzed and identified by using XRD analyses and Polaroid microscope. The results reflect the following minerals according to their average relative dominant, quartz 58.6%, feldspars 17.3%, and calcite 15.4%, with small amount of gypsum 5.5%. The clay minerals (chlorite, illite, montmorillonite, palygorskite, and kaolinite) were recognized. The analyses of heavy minerals percentages by using the microscope were performed. The results of pollen distribution, in descending order, were Chenopodiaceous, Graminea, Pine, Artemisia, Palmae, Olea, and Typha (reaching 79%, 69%, 63%, 53%, 17%, 9%, and 7% of the counted pollen grains, respectively). The results of microorganisms (i.e., isolated bacteria and fungi), in descending order, were the gram-positive Bacillus species (42.9%), Aspergillus species plus Candida albicans (13.8%), and (8.4%), the gram-negative rods, Escherichia coli (9.5%), the gram-positive Cocci streptococcus pneumonia (6.7%), then the gram-negative rod Enterobacter cloacae (4.3%), Staphylococcus epidermidis, and Staphylococcus (3.9%) and (1.9%). The remaining Gram-negative microorganisms were Pseudomonas aeruginosa (2.7%). Regarding the viral etiology, there is no viral isolate among the work results. The allergens commonly associated with dust storms include fungal spores, plant and grass pollens, and organic detritus represent agricultural area pollen grains.
Eight subsurface sections and a large number of thin sections of the Mishrif Limestone were studied to unravel the depositional facies and environments. The allochems in the Mishrif Formation are dominated by bioclasts, whereas peloids, ooids, and intraclasts are less abundant. The sedimentary microfacies of the Mishrif Formation includes mudstone, wackestone, packstone, grainstone, floatstone, and rudstone, which have been deposited in basinal, outer shelf, slop followed by shoal reef and lagoonal environments. The formation displays various extents of dolomitization and is cemented by calcite and dolomite. The formation has gradational contact with the underlying Rumaila Formation but is unconformably overlain by the Khasib Formation. The unconformity is recognized because the skeletal grains are dominated by Chaophyta (algae), which denotes the change of environment from fully marine to lacustrine environment. Thus, the vertical bioclast analysis indicates that the Mishrif Formation is characterized by two regressive cycles, which control the distribution of reservoir quality as well as the patterns of calcite and dolomite cement distribution. Mishrif Formation gradationally overlies Rumaila Formation. This was indicated by the presence of the green parts of Chaophyta (algae) as main skeletal grains at the uppermost part of well Zb-47, which refer to lacustrine or fresh water environment. Petrographical study shows that the fossils, peloids, oolitis, and intraclasts represent the main allochem. Calcite and dolomite (as diagenetic products) are the predominant mineral components of Mishrif Formation. Fossils were studied as an environmental age and facial boundaries indicators, which are located in a chart using personal computer programs depending on their distributions on the first appearance of species. Fifteen principal sedimentary microfacies have been identified in the Mishrif Formation, which includes lime mudstone, mudstonewackestone, wackestone, wackestone-packstone, packstone, packstone-grainstone, grainstone-floatstone, packstone-floatstone, packstone-rudstone, and wackestone-floatstone. Markov chain analysis has been used to study the transitional pattern of different microfacies types vertically in each well and laterally in all wells as a composite section. The vertical analysis indicates that the Mishrif Formation characterized by two regressive cycles, the main one started with basinal or outer shelf environment, slop environment followed by shoal or reefal environment, and ended with a lagoonal environment. The lateral analysis shows the same regressive cycle, and by using the lithofacies association concepts, we built the depositional model of the Mishrif Formation environment.
The Tigris River is the second-longest river in Western Asia and runs through heavily populated areas, especially in Baghdad city with nearly 8 million inhabitants. The water demand is at its highest levels, nevertheless the Tigris discharge has severely declined in the last decades; combined with the fact that the wastewater quantities are increasing, and the wastewater treatment plants are experiencing a deficiency. Four sites were chosen: the Tharthar-Tigris Canal which is located in the north part of Baghdad city, Baghdad city, the Diyala River conjunction with the Tigris River site, and Al-Azizziyah site in the south of Baghdad city near Kut government, to determine the effect of the decreasing Tigris River flow on the water quality and to identify the sources of pollution. In this research, the used method evaluates the concentration of the contaminants along the course of the Tigris River to determine the source of the contaminants as the novelty of this research. The data include the discharge of The Tigris River, a hydrochemical analysis, such as major ions and trace elements, and biological parameters (BOD5, COD, E. coli bacteria, and coliform bacteria MPN/100 mL) as contamination indicators. Multivariate statistical techniques (factor analysis) were applied to evaluate spatial variations, for the years 2005 to 2020, and Phreeqc software was used to assess the saturation indices determine the dominant geochemical processes source responsible for surface water quality. The dominant minerals of the Tigris River were gypsum, anhydrite, and halite. The Tigris River is within the permissible limits for drinking, except at the Tharthar-Tigris Canal and Diyala River, and the main water quality deterioration factors of the Tigris River were recognized as: total dissolved solids, E. coli bacteria, fecal coliform bacteria, BOD5, and COD. By applying the SPSS program, two factors were identified. The first anthropogenic factor discharged into the river represents 71.27% of the variance and is comprised of agricultural land wastewater and sewage water. While the second factor represents 17.02%, indicated by the variables Ca2+, K+, Mg2+, and SO42−. This factor accounts for the chemical weathering of rocky components. It is recommended that a periodic monitoring system is needed to. follow up on pollution levels and water quality for the Tigris River, by conducting seasonal surveys.
The shells of Mytilus edulis in the Tay estuary, Scotland, show mean aragonite contents of 55%, but in one zone the average aragonite proportion is only 45%. Comparison with data for Mytilus edulis from other regions indicates the temperature and salinity are not the only significant determinants of the aragonite/calcite ratio. Elimination of other variables suggests that sewage discharges may influence the mineralogy of the shell secreted by Mytilus edutis in the relatively nutrient-enriched areas.
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