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Brazilian Archives of Biology and Technology

Print version ISSN 1516-8913On-line version ISSN 1678-4324

Braz. arch. biol. technol. vol.51 no.2 Curitiba Mar./Apr. 2008

http://dx.doi.org/10.1590/S1516-89132008000200020 

ENGINEERING AND TECHNOLOGY

 

Microbiological and physicochemical treatments applied to metallurgic industry aiming water reuse

 

 

Antonio Roberto Crystal BelloI; Dejanira de Franceschi de AngelisI, *; Roberto Naves DomingosII

IDepartamento de Bioquímica e Microbiologia; Instituto de Biociências; Universidade Estadual Paulista - UNESP; Rio Claro - SP - Brasil
IIDepartamento de Física; Instituto de Geociências e Ciências Exatas; Universidade Estadual Paulista – UNESP; dangelis@rc.unesp.br; Av 24A nº1515; 13506-900; Rio Claro - SP - Brasil

 

 


ABSTRACT

A study was conducted on the reuse of the water in a system composed of a sewage treatment plant (STP) using prolonged aeration with activated sludge and a compact water treatment plant (CWTP) in a metallurgic industry. The processes for obtaining the water for reuse were microbiological and physicochemical. The domestic sewage was then pumped to the STP, where biological flocks were formed and clarified water was obtained. The efficiency of the microbiological process in the STP was evaluated for removal of biochemical oxygen demand (BOD), chemical oxygen demand (COD) and sedimentary solids (SS). The efficiency of physicochemical processes for clarifying the water and disinfection was evaluated through analysis of pH, turbidity, color, aerobic heterotrophic bacterial count, free chlorine, hardness, alkalinity, chlorides, sulfates and dissolved total solids (DTS). In the reuse of the water, acute toxicity for the microcrustaceans Daphnia similis was also evaluated.

Key words: Water, reuse, sewage, microorganisms, disinfection


RESUMO

Estudou-se o reuso de água de um sistema composto por estação de tratamento de esgoto (ETE) com aeração prolongada e lodo ativado, e em uma estação compacta de tratamento de água (ECTA) de uma indústria metalúrgica.

Os processos para obtenção da água de reuso foram: microbiológico e físico-químico. O esgoto doméstico foi bombeado para a ETE, onde houve formação de flocos biológicos e água clarificada. Avaliou-se a eficiência do processo microbiológico da ETE mediante a remoção de demanda bioquímica de oxigênio (DBO), demanda química de oxigênio (DQO) e sólidos sedimentáveis (SS). A eficiência do processo físico-químico de clarificação e desinfecção foi avaliada mediante análises de pH, turbidez, cor, contagem de bactérias heterotróficas aeróbias, cloro livre, dureza, alcalinidade, cloretos, sulfatos, sólidos totais dissolvidos (STD). Na água de reuso além desses parâmetros avaliou-se a toxicidade aguda ao microcrustáceo Daphnia similis.


 

 

INTRODUCTION

Domestic sewage contains, on the average, 99.9% water and only 0.1% solids, with approximately 75% of these composed of the organic matter from the decomposition process. Sewage treatment plants use biological, physical and chemical processes to remove suspended and dissolved solids present in the sewage (Nuvolari et al., 2003). The activated sludge process is widely utilized for the treatment of domestic and industrial effluents. The steps involved in the biological stage of an activated sludge system are: aeration tank, sedimentation basin and sludge from recirculation (Sperling, 2002). For the success of the activated sludge process, it is necessary to maintain a mixed culture of microorganisms for the elimination of organic matter (OM), and nutrients (nitrogen and phosphorous). The heterotrophic bacteria (HB) then consume OM and form the flocks; the autotrophic bacteria eliminate the nitrogen and store the phosphorous (Trumper, 2004).

The water to be treated can contain suspended and colloidal particles. To remove these, coagulants such as aluminum sulfate, ferrous sulfate, ferric sulfate, ferric chloride, ferrous sulfate chlorinated and sodium aluminate/ aluminum sulfate are used. This stabilizes the system due to the formation of bigger clots (Vianna, 1997). The main objective of the disinfection process is to minimize the number of pathogenic microorganisms. Other processes, such as coagulation, flocculation, sedimentation and filtration can also reduce the microorganisms in the water. The main disinfectants used in the water treatment are chlorine, hypochlorite, chlorine dioxide, ozone, ultraviolet, and others (Haas et al., 1999).

The action of disinfectants involves three mechanisms: destruction of or damage to the structural organization of the cell; interference in energy level of metabolism; or interference in biosynthesis, growth, or the proper combination of several mechanisms such as protein synthesis, inhibition of coenzymes and enzymes. In the water treatment, the two types of predominant mechanisms of desinfection are oxidation, with later rupture of the cellular wall, and diffusion in the interior of cells, with consequent interference in cellular activities (Daniel et al., 2001).

Filtration results in the removal of particles in suspension, decrease in bacteriological load, and alterations in some chemical components. The process of filtration is based on four actions: mechanical filtration, sedimentation-adsorption; electrical effects, and biological changes (Macedo, 2000).

Adsorption of a substance involves accumulation at the interface between two phases, for example, liquid and solid. Adsorbents of interest in water treatment include activated carbon, adsorbent resins, and activated alumina, among other solids. Activated carbon can be used to adsorb specific organic molecules that cause taste and odor, mutagenicity and toxicity (Vernon and Summers, 1999).

Some microorganisms, such as Giardia lamblia and Cryptosporidium parvum, are highly resistant to disinfection, so studies have been done with fast filtration, slow filtration of sand, and filtration with membrane. The processes used most often, however, are coagulation and fast filtration, including stages of flocculation and sedimentation (Cleasby and Logsoon, 1999).

The reuse of the water can be defined as follows: After the water for a determined objective has been utilized, it can be reused after receiving appropriate treatment. The main industrial applications of treated domestic effluents are: reuse for water cooling systems, reuse for systems of steam production, reuse in industrial processes, washing of tanks and parts, washing of chimney gases - atmospheric depollution (Vitoratto and Silva, 2004).

In countries like Israel and the United States, the industrial and sewage effluents are injected back into the soil through double operation wells after being treated to refill the aquifers. Due to the abundance of water resources, Brazil has not yet adopted this practice, although it is necessary to change this mentality and consider water as a limited resource (Hespanhol, 2003).

Due to the imposition of ISO 14.000 Certifications in factories, or due to a more rigorous control by the environmental organs of the quality of water being dumped into rivers, the fact is that today, companies are concerned about the type of water that they are discarding. The evolution of water quality achieved in effluent treatment plants is generating greater awareness about the waste of discarding water after it has been treated. With this, companies began to discover alternative uses for water treated in their own industrial systems. Thus, we have entered the of " Time of Intelligent Water Use" , although it should be noted that only 1% of all water consumed in Brazil is currently reutilized (Fornari, 2005).

The objective of this study was to evaluate the reuse of the water in a metallurgic industry’s domestic sewage treatment plant composed of microbiological treatment, using activated sludge system with prolonged aeration, and physicochemical treatment using disinfection, coagulation, sedimentation and filtration.

 

MATERIALS AND METHODS

Raw sewage:

Raw sewage originates from bathrooms, kitchens, floor washing, and showers in a metallurgic industry.

Sewage treatment plant (STP)

A sewage treatment plant using prolonged aeration and activated sludge processes. The plant consists of an entrance compartment, an aeration tank, and a sedimentation basin.

Compact water treatment plant (CWTP):

Conventional Compact water treatment plant with entrance compartment, a mechanical flocculation chamber, sedimentation basin with decantation modules, and a filter with activated carbon, sand layers and gravel.

Other Equipment

Digimed pHmeter, Hach turbidimeter, Orion oximeter, Hach spectrophotometer, Quimis bacteriological incubator, Polilab Jar-Test, Hach thermoreactor, Tecnal BOD incubator, thermometer, Mettler analytical balance, Quimis vacuum pump.

Reagents and Materials

Ferric chloride solution, sodium carbonate solution, sodium hypochlorite solution, Hach reagents for analyzing residual free chlorine, COD and sulfates, kit for total aerobic heterotrophic bacterial (THB) count - Merck Microbiology Culti Dip Combi, filter paper, microcrustaceans Daphnia similis, EDTA solution, metil orange solution, hardness drain plug solution, phenolphthalein solution, black eriochrome T solution, silver nitrate solution, potassium chromate solution.

Method

The raw sewage was subjected to primary treatment composed of grating and sand compartment, and after this, was deposited in a raw sewage tank, and from this tank, was pumped into the STP for microbiological treatment by prolonged aeration and activated sludge.

With the formation of biological flocks, the sewage went to the clarifiers, resulting in clarified water and sedimented sludge. The sludge returned to the aeration tank or was removed from the system to the biodigestor and the drying beds. The clarified water receives continuous sodium hypochlorite solution (prechlorination) and then goes to the equalizer tank as according to the Fig. 1.

 

 

The water of the equalizer tank of the STP (raw water of the CWTP) was pumped to the CWTP, receiving ferric chloride solution and sodium carbonate solution. The flocculated water in continuous flow arrived into the sedimentation basin and filter. After the filter, the water received sodium hypochlorite solution as a second step in disinfection; then it was deposited in a reservoir for the reuse of water. The reuse of the water for industrial use (not potable) was pumped for use in the factory in places like cooling towers, heat exchange, and as water for moisturizers.

To evaluatesystem performance, samples were examined in a raw sewage entrance in the STP, at a STP water exit following prechlorination (equalizer tank of STP), at a CWTP water exit after the second chlorination, and in the reservoir of water intended for reuse. To verify acute toxicity for Daphnia similis microcrustaceans, water samples were collected from the reservoir.

With the objective of evaluating the efficiency of microbiological processes of the STP, the parameters pH, SS, COD and BOD5,20 of raw sewage and of STP exit water were analyzed.

In the evaluation of clarifying water and disinfection (first and second chlorination) process of the CWTP, the parameters analyzed included pH, turbidity, apparent color, residual free chlorine, alkalinity, hardness, chlorides, sulfates, DTS and acute toxicity of Daphnia similis. Three analyses were made for each parameter, and an arithmetic mean was calculated. All the analyses complied with the Standard Methods for the Examination of water and wastewater (Clesceri et al, 1998).

For the counting of the THB (UFC/mL), the Cult Dip Combi TTC Agar – Microbiology Merck tecnique was used for the formation of colonies. For the determination of BOD5,20 the Norm CETESB L5.120 (1991 - a), BOD – Method of Dilution and Incubation 20ºC, 5 days was used. For the assay of the acute toxicity for microcrustaceans Daphnia similis the Norm CETESB L5. 018 (1991 - b) – Test of Acute Toxicity with Daphnia similis was used. To obtain the percent reduction in the parameters, the expression was:

% reduction =

where

I = Value of parameter before treatment process

F = Value of parameter after treatment process

 

RESULTS AND DISCUSSION

Table 1 shows the results of the raw sewage of the STP exit water and, later, of the microbiological treatment with prolonged aeration and activated sludge. The raw sewage presented the characteristics of pH 6.3 to 7.2, SS 0.5 to 16.0 ml/l, COD 326 to 1131 mg/l O2 and BOD5,20 100 to 608 mg/l O2. The STP exit water in the equalization tanks after prechlorination presented these values in the following parameters: pH 6.7 to 7.8, SSD 0.0 to 0.8 mL/l, COD 5 to 65 mg/L O2 and BOD5,20 1 to 17 mg/l O2. The average percentage of organic load removal that occurred in the STP by the action of microorganisms was of SS 91.0% (standard deviation, s = 9.3), COD 96.7% (s = 2.2) and BOD5,20 97.5 % (s = 1.6). The samples of STP exit water collected after chlorination with sodium hypochlorite solution (equalization tank - raw water of CWTP) presented physicochemical parameters with the following values: pH 6.7 to 7.8, turbidity 2.3 to 13.5 NTU, apparent color 50 to 237 PtCo, residual free chlorine 0.05 to 2.02 mg/l Cl2, total alkalinity 55 to 178 mg/l CaCO3, hardness 79 to 116 mg/l CaCO3, chlorides 139 to 182 mg/l Cl -, sulfates 88 to 122 mg/l SO42- and DTS 927 to 1224 mg/l. After the physicochemical process in the CWTP of prechlorination, coagulation, flocculation, filtration, adsorption and second chlorination, as shown Fig. 1, the water samples collected presented parameters with the following values: pH 7.5 to 8.0, turbidity 0.33 to 1.20 NTU, apparent color 10 to 30 PtCo, residual free chlorine 0.08 to 1.78 mg/l Cl2, total alkalinity 67 to 198 mg/l CaCO3, hardness 76 to 108 mg/l CaCO3, chlorides 160 to 205 mg/l Cl-, sulfates 90 to 124 mg/l SO42- and DTS 956 to 1248 mg/l. In the process used in the CWTP, it was observed a decreasing of turbidity and apparent color of an average of 85.7% (s = 5.8) and 78.2% (s = 6.6), respectively, were observed. The elevation of pH and alkalinity of this water was a function of the addition of the sodium carbonate solution to adjust the pH of coagulation. The increase in the values of the chloride was due to the dosage of the ferric chloride coagulant and the sodium hypochlorite solution.

 

 

The alkalinity and pH of this water were kept at these levels with the objective of avoiding corrosion in the industrial water reutilization system. The turbidity values of most of the samples remained between 0.50 and 0.65 NTU, what contributed to assuring the removal of enteroviruses, cysts of Giardia spp and oocysts of Cryptosporidium sp, since the process of chlorination was inefficient in eliminating them.

The reuse of the water in the reservoir after stabilization presented low free residual chlorine. The likely reasons were: chlorine evaporation, chlorine consumption in the oxidation of the remaining organic matter and elimination of microorganisms. The reservoir has a residence time of 36 hours.

For the acute toxicity tests, samples were collected from the reuseable water in the reservoir, and tested in the Norm CETESB L5.018 (1991–b). The water presented physicochemical qualities within the limits of table 3, and the results of three sample tests were of null toxicity.

 

 

 

 

ACKNOWLEDGEMENTS

We thank CB Consultoria e Treinamento S/C Ltda. for the technical support given to the project and the environmental employees of the metallurgic industry where the study of the water reuse system was conducted.

 

REFERENCES

Cetesb (1991-a), Companhia de Tecnologia e Saneamento Ambiental, Demanda Bioquímica de Oxigênio (DBO), Método da Diluição e Incubação 20 graus centígrados 5 dias, Norma Técnica L5.120, São Paulo.         [ Links ]

Cetesb (1991-b), Companhia de Tecnologia e Saneamento Ambiental, Água – Teste de Toxicidade Aguda com Daphnia similis Claus, 1876 (Cladocera Crustácea) Norma Técnica L5.018, 33 p., São Paulo.         [ Links ]

Cleasby, J. L., Logsoon, G.S. (1999), American Water Works Association Water Quality and Treatment, fifth edition, New York, Mc GRAW - HILL, INC, USA, p.8.1 a 8.91.         [ Links ]

Clesceri, L.S., Greenberg, A.E.; Eaton, A.D. (1998), Standard Methods for the Examination of Water and Wastewater, - Publication office: American Public Health Association, American Water Works Association Water Environment Federation Publication, 20Th edition, Washington DC.         [ Links ]

Daniel, L.A., Brandão, C.C.S., Guimarães, J.R., Libânio, M., Deluca, S.J. (2001), Processos de Desinfecção e Desinfetantes Alternativos na Produção de Água Potável. Prosab - Programa de Pesquisa em Saneamento Básico - São Carlos (SP), p.1 a 65.         [ Links ]

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Hespanhol, I. (2003), Potencial de Reuso de Água no Brasil: Agricultura, Indústria, Município e Recarga de Aqüíferos – Reuso de Água, 1ª edição, Editora Manole, São Paulo.         [ Links ]

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Sperling, M.V. (2002), Princípios do Tratamento Biológico de Águas Residuárias – Princípios Básicos do Tratamento de Esgotos, DESA – Departamento de Engenharia Sanitária e Ambiental, UFMG - Universidade Federal de Minas Gerais, vol. 4, 2ª edição ampliada, p. 11 a 38, Belo Horizonte.         [ Links ]

Trumper, S. (2004), Bacterias Filamentosas en Tratamiento de Aguas Servidas; Revista Ecoamerica; Edición 43, Chile, disponible en http://www.ecoamerica.cl/main/        [ Links ]

Vernon, LS., Summers, R. S. (1999), Water Quality and Treatment – A handbook of Community Water Supplies, Chapter 3 – Adsorption of Organic Compounds, American Water Works Association, Mc Graw – Hill, p. 13.1 – 13.13, New York.         [ Links ]

Vianna, M.R. (1997), Hidráulica Aplicada às Estações de Tratamento de Água, 3ª edição, Imprimatur Artes Ltda., Minas Gerais.         [ Links ]

Vitoratto, E.; Silva, J.O.P. (2004), Reuso da Água na Indústria, Informativo CRQ IV Conselho Regional de Química 4ª região, Páginas and Letras Editora e Gráfica Ltda., p. 10 e 11, São Paulo.         [ Links ]

 

 

Received: April 17, 2006;
Revised: November 13, 2006;
Accepted: October 10, 2007.

 

 

* Author for correspondence

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