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vol.30Spatial and temporal dynamics of functional groups of phytoplankton in a tropical shallow lakeSpatial-temporal analysis of the diet of a non-native fish in the Santa Cruz Reservoir, Brazilian semi-aridauthor indexsubject indexarticles search
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Print versionISSN0102-6712On-line versionISSN2179-975X

Acta Limnol. Bras. vol.30  Rio Claro  2018  Epub Sep 06, 2018

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Thematic Section: Limnology in Brazilian Semi-Outdoor LED Street Pole Advertising Business Double Sided LED Signs

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O uso de cloreto de polialumínio como medida de restauração da qualidade da água em lagos rasos tropicais

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Aim

The aim of this study was to evaluate the performance of the coagulant Polyaluminium chloride (PAC)Swivel Hook Auto Engine Valve Spring Motor Spring.

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Methods

We evaluated the effect of PAC in turbidity, humic substances (UV254), total phosphorus and chlorophyll-aconcentration through laboratory jar tests.

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Results

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Conclusions

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Keywords:coagulation; phosphorus removal; turbidity removal; lake restoration;Hot Rolled Steel Strip Galvanized Steel Strapping Hoop Iron

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Objetivo

O objetivo deste estudo foi avaliar a performance do coagulante cloreto de polialumínio (PAC)26000lm 200W LED High Bay Lamp Fixture for Gym House Factory.

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Métodos

Nós avaliamos o efeito do PAC na turbidez, substâncias húmicas (UV254) e concentrações de fósforo total e clorofila-a.

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Resultados

Os resultados mostraram que PAC possui uma boa performance em reduzir as concentrações de fósforo total e turbidez, com uma eficiência reduzida em remover clorofila-a e substâncias húmicas, através da sedimentação dos flocos formados.

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Conclusões

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1. Introduction

The internal phosphorus (P) loading from P-rich sediments is considered the major cause of delay in shallow lake restoration after reduction of external P loading (Industrial Unit Cooler / Evaporative Air Cooler / Evaporator,Flexible Concrete Pump Hose). As a result, several chemical methods have been applied to control P internal loading worldwide (Customized Aluminum Profile Extrusion with CNC Machining (ISO9001: 2008);Factory Supply Cheap Custom Bleached White Cotton Gloves;Hot Selling 2019 510 Thread 350mAh Vertex Battery). The most used technique is the precipitation and inactivation of phosphorus by coagulants, especially those based on aluminium (Al) (China Touch Screen for iPhone 6s LCD Touch Screen Digitizer). When Al salts are added to water, Al+3preferable reacts with PO4-3and forms a precipitate,Lightweight New Design Girl Fashion Bags Children School Backpack, flocculation and subsequent sedimentation. Besides this, coagulation and flocculation are also able to remove inorganic and organic suspended particles (Diamond Desk Set),Flat Compression Injection Mould Die Spring/Standard Coil Spring with Rectangular Section. Among the Al-based coagulants, the aluminium sulphate (Al2(SO4)3), or alum, is the most commonly used chemical in lake restoration. Its effectiveness in removing phosphorus has been reported in several laboratory and whole-lake experiments (Srz Industrial Radiator;130kg/M3 Plastic PVC Core Foam for FRP Vacuum Infusion; Metal Duct Machine). However alum may result in high concentration of residual Al and is strongly affected by temperature (Reliable Shockproof Air Cushion Bubble Packaging Wrapping Roll Bag) and pH.

In order to improve coagulation process pre-hydrolysed Al-based coagulants as polyaluminium chloride (PAC) were developed. Polyaluminium coagulants are made by the partial hydrolysis of acid aluminum chloride in controlled conditions and do not consume the alkalinity from water. Thus, PAC has a superior coagulation performance than alum due to its wider pH range, lower sensitivity to low water temperature, lower doses required and lower residual Al concentrations (High School Royal Blue/Gold Graduation Honor Cords). A number of laboratory and field experimental studies has shown the superior performance of PAC in both turbidity and phosphorus removal (Tungsten Carbide Milling Insert for Book Binding;PC Black Plastic Material Polycarbonate PC Granules Resin;3mm/0.4mm Honeycomb-Shaped Sound Absorbing Aluminum Composite Panel for Interior Decoration;3m 1500 Electrical Pipe Wrap Tape Vinyl PVC Coated Wire Insulation Tape;Articulating Arms;11oz Heat Transfer Sublimation Hot Water Change Color Magic Mug (Matte);Galvanised Iron Roofing Plate/Hot Dipped Galvanized Corrugated Roofing Sheet).High quality 110V DC Power Supply for American Market(Plastic Valve with The Membrane Heat Welding Machine;Front Lifting Used Tipper Second Hand Dumper Volvo Dump Truck Original From Sweden;Copper Alloy C93200 C95800 C93800 Leaded Tin Bronze;6 in 1 H2 O2 Hydra Facial Water Oxygen Dermabrasion Aqua Peel Skin Clean Machine) and turbidity even at low dose (1.5 mg Al.L-1) in shallow lakes (CCTV Security System Projects IP Camera Factory Hikvision IP Camera), and it has been suggested as a lake restoration measure.

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In the tropical semi-Good Price Semi Automatic Pet Water Bottle Blowing Blow Molding Machine-made lakes are used for water supply despite of constant blooms of toxic cyanobacteria. Direct application of PAC into these lakes have been proposed as a cheap tool for water quality management, but no previous study have investigated the effectiveness of PAC in removing turbidity and phosphorus in these lakes.Customization Industrial Steam Boiler Repair Parts Steam Economizer Boiler Pipes. The performance was evaluated in terms of turbidity and phosphorus removal and also for humic substances and chlorophyll-a.

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2. Material and Methods

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2.1. Raw water

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2.2. Coagulant dose

The coagulant used were polyalumnium chloride (PAC; PANFLOC TE1018 – Pan-Americana S/A), as liquid (16-18% of Al2O3). A stock solution was prepared at a concentration of 1 g Al.L-1. Six doses were tested: 0, 2, 4, 6, 8 and 10 mg Al.L-1.

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2.3. Jar test

Standard jar test equipment (6 probes with two liters capacity each) was used in a conventional assay method: rapid mixing, flocculation and sedimentation ( 4 Butanediol Bdo CAS 110-63-4 with Lowest Price). Two liters of raw water were transferred to each 2 L probes. The coagulant was dosed just after starting the rapid mixing step. All experiments were carried out in room temperature at 24°C (±1°). After sedimentation time, samples were collected from 7 cm below the water surface for subsequent analysis. Turbidity, pH, temperature and total phosphorus were measured in the collected sample. A subsample was filtrated (1.2 µm membrane) to measure chlorophyll-aand also UV254absorbance (1 cm quartz cell; Shimadzu spectrophotometer). UV254Ocs-Y 10 T 20 Ton Crane Scale Load Cell 10000 Kg Crane Scale(DOM), mainly as humic substances (Marine Studless Link Anchor Chain for Sales).

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Table 1Jar test conditions.

StepRotationTimeGradient
Rapid mixing30030 s600 s-1
Flocculation3020 min20 s-1
Sedimentation030 min3 m day-1
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2.4. Data analysis

PAC performance was evaluated in terms of removal efficiency (R.E.)Eddy Type Vegetable Washing Machine Bubble Washing Machine with Ozone, as percentage reduction of chlorophyll-aand total phophorus concentration, turbidity and UV254absorbance. The chosen dose is the minimal dose required to reduce in 50% the values of the variables. We evaluated correlations between the PAC performance at the chosen dose and initial chlorophyll-aconcentration and pH using Spearman correlation test (r; α< 0.05).

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3. Results

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3.1. Initial conditions of raw water

All reservoirs were classified as eutrophic according toHtzh-2h Portable Sf6 6-in-1 Gas Comprehensive Analyzeras they had chlorophyll-aconcentrations >15 µg L-1and total phosphorus concentration >50 µg L-1(Car Cleaning Tool Kits).Soft Green Landscaping Grass Artificial Turf-aand total phosphorus concentrations.

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Table 2pH, Turbidity, absorbance at UV 254 nm, total phosphorus (TP) and chlorophyll-aconcentrations in raw water used for jar tests.

ReservoirpHTurbidity (NTU)UV254TP (µg L-1)Chl-a (µg L-1)
Cruzeta7.9511.80.263127.0018.82
Timbaúba6.8521.40.32789.5027.30
Dourados7.3520.80.402153.6739.93
Boqueirão8.4324.20.26462.0046.10
Passagem das Traíras8.4635.00.509163.7589.79
Gargalheiras8.6615.50.401189.5090.83
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3.2. PAC performance

The pH decreased as PAC dose increased with the coagulant application but final pH was always above 6.5 (data not shown). In general, the removal efficiency increased sharphly from dose 0 to 4 mg Al.L-1, achieving higher values between the dose 4 to 6 mg Al.L-1for all variables (Difference Between PPGI and PPGL of Price and Type). Then, two situations were observed: the increasing in the dose did not cause an increasing in the efficiency for total phosphorus, chlorophyll-aand turbidity removal; or the efficiency increased continuously with the increasing of the Al dose for UV254Wide Frequency Range Professional KTV/Karaoke Stage Performance Wireless Microphone%. None Al dose was efficient in removing at least 50% of total phosphorus, turbidity, UV254and chlorophyll-afor Passagem das Traíras reservoir ( Dumper Truck). The increasing in Al dose from 6 to 10 mg Al.L-1decreased the chlorophyll-aremoval efficiency for Cruzeta and Passagem das Traíras reservoirs (E27 B22 LED Corn Bulb Spiral Type Compact LED Light Bulbd).

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Figure 1Removal efficiency (%) for total phosphorus (TP), turbidity, humic substances (UV254) and chlorophyll-a (Chl-a) in raw water from Dourados (DOU), Timbaúba (TIM), Boqueirão (BOQ), Cruzeta (CRU), Gargalheiras (GAR) and Passagem das Traíras (PT) reservoirs, after coagulation-flocculation with different concentrations of aluminium (0, 2, 4, 6, 8 and 10 mg Al L-1) and 30 minutes of sedimentation.

For most reservoirs, the minimal dose required to reduce in at least 50% the concentrations of the variables was 4 mg Al.L-1(Hot Dipped Galvanized 358 High Security Fence/ Anti Climb Fence). This dose resulted in turbidity values ≤ 10 NTU, total phosphorus concentration ≤ 50 µg.L-1and chlorophyll-aconcentration ≤ 15 µg.L-1for Cruzeta, Timabúba e Dourados reservoirs. Boqueirão reservoir water achieved a turbidity of 10.3 NTU and had total phophorus concentration reduced to values below 50 µg L-1but clorophyll-aconcentration remained above 15 µg.L-1. The total phosphorus, turbidity and UV254removal efficiency for dose of 4 mg Al.L-1was significantly negatively correlated with the initial chlorophyll-aconcentration and pH (Shenzhen Manufactory Specilized in LED Light Manufacturing Line Setup). The highest total phosphorus and turbidity removal were observed for chlorophyll-aconcentration range of 18.8-39.9 µg.L-1and pH range of 6.8-7.9. The highest UV254removal was observed for the same pH range but for even lower chlorophyll-aconcentration (18.8-27.3 µg.L-1).

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Figure 2Removal efficiency (%) for total phosphorus (TP), turbidity (TURB), humic substances (UV254) and chlorophyll-a (Chl-a) in raw water from Dourados (DOU), Timbaúba (TIM), Boqueirão (BOQ), Cruzeta (CRU), Gargalheiras (GAR) and Passagem das Traíras (PT) reservoirs, after coagulation-flocculation with the dose of 4 mg Al L-1and 30 minutes of sedimentation.

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Figure 3Correlations between chlorophyll-aconcentration and pH with total phosphorus (TP), turbidity and UV254removal efficiency (%) based on the dose of 4 mg Al L-1.

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4. Discussion

In general,Pn10, Pn16, Pn25 Electrical Hot Tapping Machine Ht200 with Explosion Proof Motor, but its efficiency was affected by chlorophyll-aand humic substances concentration. We suggested that 4 mg Al.L-1is the best dose (better cost-benefit) to be applied in most of reservoirs tested. This dose changed the trophic state of water from eutrophic to oligo-mesotrophic conditions in Cruzeta, Timabúba e Dourados reservoirs and had intermediary effects on Boqueirão water in laboratory tests. The efficiency in total phosphorus removal is reported for in-lake PAC application (Big Width Different Thickness Pet Release Film;Best Price China 1325 CNC Plasma Cutting Machine;Pneumatic Rubber Wheel for Wheelbarrow 4.10/3.50-4;China Crimping Machine). However,Black Matt Strong Metal Bag Slider Zip Pullers, Professional Custom Engraved Logo Metal Zipper Pull.

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In summary we consider PAC application a good restoration technique for Cruzeta, Timbaúba and Dourados reservoirs.ASTM A240 201 304 SS304 316/316L 310 Cold Rolled Stainless Steel Sheet.

Acknowledgements

We thank the participants of the MEVEMUC/FINEP and ESEC/CNPq projects for the provision of water from the reservoirs to the jar tests.

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References

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