ArticlePDF Available

Physico-chemical parameters for testing of water - a review

Authors:
  • University of Technology and Applied Sciences

Abstract

People on globe are under tremendous threat due to undesired changes in the physical, chemical and biological characteristics of air, water and soil. Due to increased human population, industrialization, use of fertilizers and man-made activity water is highly polluted with different harmful contaminants. Natural water contaminates due to weathering of rocks and leaching of soils, mining processing etc. It is necessary that the quality of drinking water should be checked at regular time interval, because due to use of contaminated drinking water, human population suffers from varied of water borne diseases. The availability of good quality water is an indispensable feature for preventing diseases and improving quality of life. It is necessary to know details about different physico-chemical parameters such as color, temperature, acidity, hardness, pH, sulphate, chloride, DO, BOD, COD, alkalinity used for testing of water quality. Heavy metals such as Pb, Cr, Fe, Hg etc. are of special concern because they produce water or chronic poisoning in aquatic animals. Some water analysis reports with physic-chemical parameters have been given for the exploring parameter study. Guidelines of different physic-chemical parameters also have been given for comparing the value of real water sample. Keyword: Water, Physico - chemical, Parameters, Hardness, BOD, Heavy metals.
INTERNATIONAL JOURNAL OF ENVIRONMENTAL SCIENCES Volume 3, No 3, 2012
© Copyright by the authors - Licensee IPA- Under Creative Commons license 3.0
Review article ISSN 0976 4402
Received on October 2012 Published on November 2012 1194
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
Department of Engineering Chemistry, Bharati Vidyapeeth’s College of Engineering, Near
Chitranagari, Kolhapur, Maharashtra, 416013 (INDIA)
pnpatil_chem@rediffmail.com
ABSTRACT
People on globe are under tremendous threat due to undesired changes in the physical,
chemical and biological characteristics of air, water and soil. Due to increased human
population, industrialization, use of fertilizers and man-made activity water is highly polluted
with different harmful contaminants. Natural water contaminates due to weathering of rocks
and leaching of soils, mining processing etc. It is necessary that the quality of drinking water
should be checked at regular time interval, because due to use of contaminated drinking water,
human population suffers from varied of water borne diseases. The availability of good
quality water is an indispensable feature for preventing diseases and improving quality of life.
It is necessary to know details about different physico-chemical parameters such as color,
temperature, acidity, hardness, pH, sulphate, chloride, DO, BOD, COD, alkalinity used for
testing of water quality. Heavy metals such as Pb, Cr, Fe, Hg etc. are of special concern
because they produce water or chronic poisoning in aquatic animals. Some water analysis
reports with physic-chemical parameters have been given for the exploring parameter study.
Guidelines of different physic-chemical parameters also have been given for comparing the
value of real water sample.
Keyword: Water, Physico - chemical, Parameters, Hardness, BOD, Heavy metals.
1. Introduction
Water is one of the most important and abundant compounds of the ecosystem. All living
organisms on the earth need water for their survival and growth. As of now only earth is the
planet having about 70 % of water. But due to increased human population, industrialization,
use of fertilizers in the agriculture and man-made activity it is highly polluted with different
harmful contaminants. Therefore it is necessary that the quality of drinking water should be
checked at regular time interval, because due to use of contaminated drinking water, human
population suffers from varied of water borne diseases. It is difficult to understand the
biological phenomenon fully because the chemistry of water revels much about the
metabolism of the ecosystem and explain the general hydro - biological relationship
(Basavaraja Simpi et al. 2011).
The availability of good quality water is an indispensable feature for preventing diseases and
improving quality of life. Natural water contains different types of impurities are introduced
in to aquatic system by different ways such as weathering of rocks and leaching of soils,
dissolution of aerosol particles from the atmosphere and from several human activities,
including mining, processing and the use of metal based materials (Ipinmoroti and Oshodi
1993, Adeyeye 1994, Asaolu 1997). The increased use of metal-based fertilizer in agricultural
revolution of the government could result in continued rise in concentration of metal
pollutions in fresh water reservoir due to the water run-off. Also faucal pollution of drinking
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1195
water causes water born disease which has led to the death of millions of people. ( Adefemi
and Awokunmi, 2010).
People on globe are under tremendous threat due to undesired changes in the physical,
chemical and biological characteristics of air, water and soil. These are related to animal and
plants and finally affecting on it (Misra and Dinesh 1991). Industrial development (Either
new or existing industry expansion) results in the generation of industrial effluents, and if
untreated results in water, sediment and soil pollution (Fakayode and Onianwa 2002,
Fakayode 2005).
Having mainly excessive amounts of heavy metals such as Pb, Cr and Fe, as well as heavy
metals from industrial processes are of special concern because they produce water or chronic
poisoning in aquatic animals (Ellis 1989). High levels of pollutants mainly organic matter in
river water cause an increase in biological oxygen demand (Kulkarni 1997), chemical oxygen
demand, total dissolved solids, total suspended solids and fecal coli form. They make water
unsuitable for drinking, irrigation or any other use (Hari 1994).
There are trends in developing countries to use sewage effluent as fertilizer has gained much
importance as it is considered a source of organic matter and plant nutrients and serves as
good fertilizer (Riordan 1983). Farmers are mainly interested in general benefits, like
increased agriculture production, low cost water source, effective way of effluent disposal,
source of nutrients, organic matter etc, but are not well aware of its harmful effects like heavy
metal contamination of soils, crops and quality problems related to health. Research has
proven that long term use of this sewage effluent for irrigation contaminates soil and crops to
such an extent that it becomes toxic to plants and causes deterioration of soil (Quinn 1978,
Hemkes1980). This contains considerable amount of potentially harmful substances including
soluble salts and heavy metals like Fe2+, Cu2+, Zn2+, Mn2+, Ni2+, Pb2+. Additions of these
heavy metals are undesirable. Plants can accumulate heavy metals in their tissues in
concentrations above the permitted levels which is considered to represent a threat to the life
of humans, and animals feeding on these crops and may lead to contamination of food chain,
as observed that soil and plants contained many toxic metals, that received irrigation water
mixed with industrial effluent (Adnan Amin 2010).
The quality of ground water depends on various chemical constituents and their concentration,
which are mostly derived from the geological data of the particular region. Industrial waste
and the municipal solid waste have emerged as one of the leading cause of pollution of
surface and ground water. In many parts of the country available water is rendered non-
potable because of the presence of heavy metal in excess. The situation gets worsened during
the summer season due to water scarcity and rain water discharge. Contamination of water
resources available for household and drinking purposes with heavy elements, metal ions and
harmful microorganisms is one of the serious major health problems. The recent research in
Haryana (India) concluded that it is the high rate of exploration then its recharging,
inappropriate dumping of solid and liquid wastes, lack of strict enforcement of law and loose
governance are the cause of deterioration of ground water quality (Guptaa 2009).
Most of the rivers in the urban areas of the developing countries are the ends of effluents
discharged from the industries. African countries and Asian countries experiencing rapid
industrial growth and this is making environmental conservation a difficult task (Agarwal
Animesh 2011). Sea water contains large number of trace metals in very small concentration.
This is a challenging matrix for the analytical chemist due to the very low concentrations of
many important trace metals (Robertson 1968, Riley).
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1196
2. Physico- Chemical Parameters
It is very essential and important to test the water before it is used for drinking, domestic,
agricultural or industrial purpose. Water must be tested with different physic-chemical
parameters. Selection of parameters for testing of water is solely depends upon for what
purpose we going to use that water and what extent we need its quality and purity. Water
does content different types of floating, dissolved, suspended and microbiological as well as
bacteriological impurities. Some physical test should be performed for testing of its physical
appearance such as temperature, color, odour, pH, turbidity, TDS etc, while chemical tests
should be perform for its BOD, COD, dissolved oxygen, alkalinity, hardness and other
characters. For obtaining more and more quality and purity water, it should be tested for its
trace metal, heavy metal contents and organic i.e. pesticide residue. It is obvious that drinking
water should pass these entire tests and it should content required amount of mineral level.
Only in the developed countries all these criteria’s are strictly monitored. Due to very low
concentration of heavy metal and organic pesticide impurities present in water it need highly
sophisticated analytical instruments and well trained manpower. Following different physic
chemical parameters are tested regularly for monitoring quality of water.
2.1 Temperature
In an established system the water temperature controls the rate of all chemical reactions, and
affects fish growth, reproduction and immunity. Drastic temperature changes can be fatal to
fish.
2.2 pH
pH is most important in determining the corrosive nature of water. Lower the pH value higher
is the corrosive nature of water. pH was positively correlated with electrical conductance and
total alkalinity(Guptaa 2009). The reduced rate of photosynthetic activity the assimilation of
carbon dioxide and bicarbonates which are ultimately responsible for increase in pH, the low
oxygen values coincided with high temperature during the summer month. Various factors
bring about changes the pH of water. The higher pH values observed suggests that carbon
dioxide, carbonate-bicarbonate equilibrium is affected more due to change in physico-
chemical condition (Karanth 1987).
2.3 EC (Electrical Conductivity)
Conductivity shows significant correlation with ten parameters such as temperature , pH
value , alkalinity , total hardness , calcium , total solids, total dissolved solids , chemical
oxygen demand , chloride and iron concentration of water. Navneet Kumar et al (2010)
suggested that the underground drinking water quality of study area can be checked
effectively by controlling conductivity of water and this may also be applied to water quality
management of other study areas. It is measured with the help of EC meter which measures
the resistance offered by the water between two platinized electrodes. The instrument is
standardized with known values of conductance observed with standard KCl solution.
2.4 Carbon Dioxide
Carbon dioxide is the end product of organic carbon degradation in almost all aquatic
environments and its variation is often a measure of net ecosystem metabolism(Smith 1997,
1993, Hopkinson 1985). Therefore, in aquatic biogeochemical studies, it is desirable to
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1197
measure parameters that define the carbon dioxide system. CO2 is also the most important
green house gas on Earth. Its fluxes across the air-water or sediment-water interface are
among the most important concerns in global change studies and are often a measure of the
net ecosystem production/metabolism of the aquatic system.
There are various readily measurable parameters of aquatic carbon dioxide system: such as
pH (pCO2), total dissolved inorganic carbon (DIC) and total alkalinity (TA). Surface water
pCO2 can be measured by photometric method (DeGrandpre 1993, Wang, Z 2002) and DIC
CO2 is measured by coulometer or by an infrared CO2 analyzer (Dickson 1994). Total
Alkalinity CO2 is determined by HCl titration of the water sample to the CO2 equivalence
point.(Gran 1952).
2.5 Alkalinity
It is Composed primarily of carbonate (CO32-) and bicarbonate (HCO3-), alkalinity acts as a
stabilizer for pH. Alkalinity, pH and hardness affect the toxicity of many substances in the
water. It is determined by simple dil HCl titration in presence of phenolphthalein and methyl
orange indicators. Alkalinity in boiler water essentially results from the presence of hydroxyl
and carbonate ions. Hydroxyl alkalinity (causticity ) in boiler water is necessary to protect the
boiler against corrosion. Too high a causticity causes other operating problems, such as
foaming. Excessively high causticity levels can result in a type of caustic attack of the boiler
called "embrittlement".
2.6 Dissolved Oxygen
DO is one of the most important parameter. Its correlation with water body gives direct and
indirect information e.g. bacterial activity, photosynthesis, availability of nutrients,
stratification etc. (Premlata Vikal, 2009). In the progress of summer, dissolved oxygen
decreased due to increase in temperature and also due to increased microbial activity (Moss
1972, Morrissette 1978, Sangu 1987, Kataria, 1996). The high DO in summer is due to
increase in temperature and duration of bright sunlight has influence on the % of soluble
gases (O² & CO²). During summer the long days and intense sunlight seem to accelerate
photosynthesis by phytoplankton, utilizing CO2 and giving off oxygen. This possibly
accounts for the greater qualities of O2 recorded during summer (Krishnamurthy R, 1990).
DO in sample is measured titrimetrically by Winkler’s method after 5 days incubation at 293
K. The difference in initial and final DO gives the amount of oxygen consumed by the
bacteria during this period. This procedure needs special BOD bottles which seal the inside
environment from atmospheric oxygen.
2.7 Carbonate
Whenever the pH touches 8.3, the presence of carbonates is indicated. It is measured by
titration with standardized hydrochloric acid using phenolphthalein as indicator. Below pH
8.3, the carbonates are converted into equivalent amount of bicarbonates. The titration can
also be done pH metrically or potentiometrically.
2.8 Bicarbonate
It is also measured by titration with standardized hydrochloric acid using methyl orange as
indicator. Methyl orange turns yellow below pH 4.0. At this pH, the carbonic acid
decomposes to give carbon dioxide and water.
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1198
2.9 Biochemical Oxygen Demand (BOD)
BOD is a measure of organic material contamination in water, specified in mg/L. BOD is the
amount of dissolved oxygen required for the biochemical decomposition of organic
compounds and the oxidation of certain inorganic materials (e.g., iron, sulfites). Typically the
test for BOD is conducted over a five-day period (Milacron Marketing Co.).
2.10 Chemical Oxygen Demand (COD)
COD is another measure of organic material contamination in water specified in mg/L. COD
is the amount of dissolved oxygen required to cause chemical oxidation of the organic
material in water. Both BOD and COD are key indicators of the environmental health of a
surface water supply. They are commonly used in waste water treatment but rarely in general
water treatment. (Milacron Marketing Co.).
2.11 Sulphate
It is measured by nephelometric method in which the concentration of turbidity is measured
against the known concentration of synthetically prepared sulphate solution. Barium chloride
is used for producing turbidity due to barium sulphate and a mixture of organic substance
(Glycerol or Gum acetia) and sodium chloride is used to prevent the settling of turbidity.
2.12 Ammonia (Nitrogen)
It is measured spectroscopically at 425 nm radiation by making a colour complex with
Nessler’s reagent. The conditions of reaction are alkaline and cause severe interference from
hardness in water.
2.13 Calcium
It is measured by complexometric titration with standard solution of ETDA using Patton’s
and Reeder’s indicator under the pH conditions of more than 12.0. These conditions are
achieved by adding a fixed volume of 4N Sodium Hydroxide. The volume of titre (EDTA
solution) against the known volume of sample gives the concentration of calcium in the
sample.
2.14 Magnesium
It is also measured by complexometric titration with standard solution of EDTA using
Eriochrome black T as indicator under the buffer conditions of pH 10.0. The buffer solution
is made from Ammonium Chloride and Ammonium Hydroxide. The solution resists the pH
variations during titration.
2.15 Sodium
It is measured with the help of flame photometer. The instrument is standardized with the
known concentration of sodium ion (1 to 100 mg/litre). The samples having higher
concentration are suitably diluted with distilled water and the dilution factor is applied to the
observed values.
2.16 Potassium
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1199
It is also measured with the help of flame photometer. The instrument is standardized with
known concentration of potassium solution, in the range of 1 mg to 5 mg/litre. The sample
having higher concentration is suitably diluted with distilled water and the dilution factor is
applied to the observed values.
2.17 Chloride
It is measured by titrating a known volume of sample with standardized silver nitrate solution
using potassium chromate solution in water or eosin/fluorescein solution in alcohol as
indicator. The latter indicator is an adsorption indicator while the former makes a red colored
compound with silver as soon as the chlorides are precipitated from solution.
2.18 Silicates & Phosphate
These are also measured spectroscopically. Yellow colour is developed from the action of
phosphates and silicates on molybdate ion under strong acidic conditions. The intensity of
colour is directly proportional to the concentration of phosphate and silicates in the sample.
Phosphate complexes are reduced by weak reducing agents such as ascorbic acid or tartaric
acid (potassium antimonyl tartarate) where as silica complexes require strong reducing
conditions of hydrazine or bisulphite. The colour of reduced complex is sky blue.
Most of the physico- chemical parameters are determined by standard methods prescribed by
ASTM (2003) and APHA (1985), Trivedy and Goal (1986), Kodarkar (1992).
3. Some physico chemical analysis study of polluted water sample in India
Physico chemical parameter study is very important to get exact idea about the quality of
water and we can compare results of different physico chemical parameter values with
standard values. Aftab Begum et al.(2005) studied various physico-chemical parameters
and analysis of untreated fertilizer effluent. His result revealed that the parameters like EC,
TDS, TSS, BOD, COD and ammonia are high compared to permissible limits of CPCB
(1995), and fungal analysis showed the presence of 15 species isolated on Malt Extract Agar
(MEA) medium thereby indicating the pollutional load of the effluent. Dey Kallol et
al.(2005) studied various physio-chemical parameters on the samples drawn from the river
Koel, Shankha and Brahmani. It was observed that dilution during rainy season decreases the
metal concentration level to a considerable extent. However the enrichment of these metals
by bio-magnification and bioaccumulation in edible components produced in water is
accepted to produce a remarkable effect on the water of the river Brahamani which is of deep
public concern.
Pawar Anusha et al.(2006) has studied the bore well and dug well water samples from a
highly polluted industrial area Nacharam. Sample were collected and analysed for physico-
chemical parameters by adopting the standard methods for examination for water and waste
water. The analyzed samples obtained a high values, compared with drinking water standards.
Poonkothai and Parvatham (2005) had been studied physico-chemical and microbiological
studies of automobile wastewater in Nammakkal, Tamil Nadu, India indicated that the values
for physico-chemical parameters were on the higher side of permissible limits of BIS.
Microbiological studies revealed the presence of bacteria at high concentration and these
organisms serves as indicators for pollutants. Rokade and Ganeshwade (2005) showed high
fluctuations in the physico-chemical parameters indicating the intensity of pollution. The pH
ranged from minimum of 6.6 to maximum of 8.4, chlorides from 132.5 to 820.4mg/l,
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1200
hardness ranged from 74 to 281 mg/l, CO2 from 2.1 to 5.09, BOD from 4.437 to 112.432
mg/l, sulphates 0.192 to 5.12 mg/l, nitrates 0.5 to 1.012. The minimum pH value of 6.3 mg/l
was found during winter season and maximum of 8.93 mg/l in summer. The pH shows
general decline from upstream to downstream. CO2 was found to maximum in summer
reaching up to 55.44 mg/l and reduced to a minimum of 2.28 mg/l during rainy season. From
the data collected it can be concluded that the inverse relationship, which is known to exist
between pH and CO2 , is not existing in the present investigation(Sawane 2006).
Sharma Madhavi et al. (2005) studied ground water quality of industrial area of Kishangarh
for various physicochemical parameters seasonally without and after addition of marble
slurry in different proportions. From the study it is clear that these parameters increase with
the addition of marble slurry leading to deterioration of the overall quality of the groundwater.
Singhal et al.(2005) study reports on the treatment of pulp and paper mill effluent by
Phanerochaete chrysosporium and the same has been compared at two different pH 5.5 and
8.5. At both the pH, colour, COD, lignin content and total phenols of the effluent
significantly declined after bioremediation. However, greater decolourisation and reduction
in COD, lignin content and total phenols were observed at pH 5.5. Chavan et al. (2005) was
carried out investigation to study the different organic pollutants present in the Thane creek
water. The creek water shows high values of BOD and COD along with 15 phenolic
compounds, detergents, alcohols, ether and acetone, which are harmful to aquatic life. The
origin of this pollutants is mainly from the entry of effluents from surrounding industries.
Two major cement industries of the Ariyalur and Reddipalayam were selected and the waste
water discharged from these units were collected and subjected to analysis. The values of
different parameters were compared with the standard values given by Tamil Nadu Pollution
Control Board. The reasons for variations are analysed and remedial measures suggested
(Gnana 2005). In mineral based industry among various environmental issues the water
pollution has posed most disastrous effect and complex challenges for undertaking necessary
remedial measures. The sources of water pollution in different mineral based industries
including mining, mineral processing, integrated iron and steel plant and nonferrous metal
industries are described. Various liquid effluent treatments techniques both physiochemical
and biological have been described and discussed. The process in each case being used
commercially, have been outlined.( Jena and Mohanty 2005).
Premlata Vikal (2009) has been work out the physico-chemical characteristics of the Pichhola
lake water. He studied various parameters like air and water temperature, pH, free CO2,
dissolved oxygen, biochemical oxygen demand, chemical oxygen demand, conductivity, total
dissolved solids, hardness, total alkalinity, chloride, nitrate, phosphate and sulphate. The
results revealed that the values of conductivity, COD, and sulphate were found to cross the
standard limits in water samples. The coefficient of correlation (r) among various physico-
chemical parameters was also made.
Gupta et al (2009) were analyzed water samples from 20 sampling points of Kaithal for their
physicochemical characteristics. Analysis of samples for pH, Colour, Odour, Hardness,
Chloride, Alkalinity, TDS etc. On comparing the results against drinking water quality
standards laid by Indian Council of Medical Research (ICMR) and World Health
Organization (WHO), it is found that some of the water samples are non-potable for human
being due to high concentration of one or the other parameter. Thus an attempt has been
made to find the quality of ground water in and around Kaithal City town, suitable for
drinking purposes or not. Basawaraj simpi et al.(2011) studied monthly changes in various
physic chemical parameters of Hosahalli water tank in shimoga district Karnataka. Study
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1201
shows that all parameters are within the limit and tank water non polluted and it can be used
for domestic, irrigation and fishery purpose.
Saravanakumar and Ranjith Kumar (2011) presents paper studies about groundwater quality
of Ambattur industrial area in Chennai City. They studied parameters such as pH, total
alkalinity, total hardness, turbidity, chloride, sulphate, fluoride, total dissolved solids and
conductivity. It was observed that there was a slight fluctuation in the physico-chemical
parameters among the water samples studied. Comparison of the physico-chemical
parameters of the water sample with WHO and ICMR limits showed that the groundwater is
highly contaminated and account for health hazards for human use. Manjare et al. (2010)
were studies the Physico-chemical Parameters of Tamadalge Water Tank in Kolhapur District,
Maharashtra. Monthly Changes In Physical and Chemical Parameters Such as Water
Temperature, Transparency, Turbidity, Total Dissolved Solids, pH, Dissolved Oxygen, Free
Carbon dioxide, and Total Hardness, Chlorides, Alkalinity, Phosphate and Nitrates. Were
analyzed for a periods of one year. All Parameters were within the Permissible limits. The
results indicate that the tank is Non-polluted and can be used for Domestic and Irrigation.
Highly impure water has various effects on human being, domestic purpose as well as
industrial use. Such as human beings get affected/ infected due to presence of different
bacteria and heavy metals present in water. It may affect the different body organ and
physiological disorder. Hard water is not suitable for domestic use such as washing, bathing,
cooking as well as other purpose. Hard water is also not suitable for industrial and
agricultural use. It damages the delicate machineries and affects the quality, stability and
glossiness of the final product.
Central water commission is maintaining a three tier Laboratory system for analysis of the
parameters. The Level-I Laboratories are located at 258 field water quality monitoring
stations on various rivers of India where physical parameters such as temperature, colour,
odour, specific conductivity, total dissolved solids, pH and Dissolved Oxygen of river water
are observed . There are 24 Level-II Laboratories located at selected Division Offices to
analyse 25 different physico- chemical characteristics and bacteriological parameters of river
water.
Table 1: Different analytical water quality parameters with their analytical technique and
guideline values as per who and Indian standard
Sr.
No.
Parameter
Technique used
WHO
standard
Indian
Standard
EPA
guidelines
01
Temperature
Thermometer
-
-
-
02
Color
Visual / color kit
-
5 Hazen
units
-
03
Odour
Physiological sense
Acceptable
Acceptable
-
04
Electrical
conductivity
Conductivity meter /
Water analysis kit
-
-
2500 us/cm
05
pH
pH meter
6.5 9.5
6.5 9.5
6.5 9.5
06
Dissolved
oxygen
Redox titration
-
-
-
07
Total Hardness
Complexometric titration
200 ppm
300 ppm
< 200 ppm
08
Alkalinity
Acid Base titration
-
200 ppm
-
09
Acidity
Acid Base titration
-
-
-
10
Ammonia
UV Visible
Spectrophotometer
0.3 ppm
0.5 ppm
0.5 ppm
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1202
11
Bi carbonate
Titration
-
-
-
12
Biochemical
Oxygen
Demand
(B.O.D.)
Incubation followed by
titration
6
30
5
13
Carbonate
Titration
-
-
-
14
Chemical
Oxygen
Demand
(C.O.D.)
C.O.D. digester
10
-
40
15
Chloride
Argentometric titration
250 ppm
250 ppm
250 ppm
16
Magnesium
Complexometric titration
150 ppm
30 ppm
17
Nitrate
UV Visible
Spectrophotometer
45 ppm
45 ppm
50 mg/l
18
Nitrite
UV Visible
Spectrophotometer
3 ppm
45 ppm
0.5 mg/l
19
Potassium
Flame Photometer
-
-
-
20
Sodium
Flame Photometer
200 ppm
180 ppm
200 ppm
21
Sulphate
Nephelometer /
Turbidimeter
250 ppm
200 ppm
250 ppm
Ref.:- [WHO, USEPA, Indian Standard, National Primary Drinking Water Regulations,
Drinking Water Contaminants US EPA]
Table 2: Different analytical water quality parameters used for testing of quality of water
and their sourse of occurance and potential health effects with USEPA guidelines.
Sr.
No.
Parameter
Potential health effect
01
Turbidity
Higher level of turbidity are
associated with disease causing
bacteria’s.
02
Color
-
03
Odor
Bad odor unpleasant
04
Electrical
conductivity
Conductivity due to ionizable ions.
High conductivity increases
corrosive nature of water.
05
pH
Affects mucous membrane; bitter
taste; corrosion
06
Dissolved
oxygen
D. O. corrode water lines,
boilers and heat exchangers, at low
level marine animals cannot
survive.
07
Total
Hardness
Poor lathering with soap;
deterioration of the quality of
clothes; scale forming
08
Total
Alkalinity
Embrittlement of boiler steel.
Boiled rice turns yellowish
09
TDS
Undesirable taste; gastro-intestinal
irritation; corrosion or incrustation
10
Calcium
Interference in dyeing, textile,
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1203
11
Magnesium
paper industry etc.
12
Ammonia
Corrosion of Cu and Zn alloys by
formation of complex ions.
13
Barium
Increase in blood pressure
14
Biochemical
Oxygen
Demand
(B.O.D.)
High BOD decreases level of
dissolved oxygen.
15
Carbonate
Product imbalance
Unsatisfactory production
Short product life
16
Chloride
Eye/nose irritation; stomach
discomfort. Increase corrosive
character of water.
17
Nitrate
Effect on Infants below the age of
six months Symptoms include
shortness of breath and blue-baby
syndrome.
18
Phosphate
stimulate microbial growth,
Rancidity Mold growth
19
Sodium
-
20
Sulphate
Taste affected; gastro-intestinal
irritation. Calcium sulphate scale.
4. References
1. Adefemi S. O. and E. E. Awokunmi, (2010), Determination of physico-chemical
parameters and heavy metals in water samples from Itaogbolu area of Ondo-State,
Nigeria, African Journal of Environmental Science and Technology, 4(3), pp 145-148.
2. Adeyeye EI, (1994), Determination of heavy metals in Illisha Africana, associated
Water, Soil Sediments from some fish ponds, International Journal of Environmental
Study, 45, pp 231-240.
3. Adnan, Amin, Taufeeq, Ahmad, Malik, Ehsanullah, Irfanullah, Muhammad, Masror,
Khatak and Muhammad, Ayaz, Khan, (2010), Evaluation of industrial and city
effluent quality using physicochemical and biological parameters, Electronic Journal
of Environmental, Agricultural and Food Chemistry, 9(5), pp 931-939.
4. Aftab, Begum, S. Y, Noorjahan, C. M., Dawood, Sharif, S, (2005), Physico-chemical
and fungal analysis of a fertilizer factory effluent, Nature Environment & Pollution
Technology, 4(4), 529-531.
5. Agarwal, Animesh and Manish, Saxena, (2011), Assessment of pollution by
Physicochemical Water Parameters Using Regression Analysis: A Case Study of
Gagan River at Moradabad- India, Advances in Applied Science Research, 2(2), pp
185 -189.
6. APHA, (1985), Standard Methods For Examination of Water and Wastewater, 20th
Edition, American Public Health Association, Washington D. C.
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1204
7. ASTM International, (2003), Annual Book of ASTM Standards, Water and
Environmental Technology v. 11.01, West Conshohocken, Pennsylvania,pp 6-7.
8. Basavaraja, Simpi, S. M., Hiremath, K. N. S. Murthy, K. N. Chandrashekarappa, Anil
N. Patel, E.T.Puttiah, (2011), Analysis of Water Quality Using Physico-Chemical
Parameters Hosahalli Tank in Shimoga District, Karnataka, India, Global Journal of
Science Frontier, Research, 1(3), pp 31-34.
9. Chavan, R. P., Lokhande, R. S., Rajput, S. I., (2005), Monitoring of organic pollutants
in Thane creek water, Nature Environment and Pollution Technology, 4(4), pp 633-
636.
10. DeGrandpre, M. D, 1993. Measurement of seawater pCO2 using a renewable-reagent
fiber optic sensor with colorimetric detection, Analytical Chemistry, 65, pp 331-337.
11. Dey, Kallol, Mohapatra, S. C., Misra, Bidyabati, (2005), Assessment of water quality
parameters of the river Brahmani at Rourkela, Journal of Industrial Pollution Control,
21(2), 265-270.
12. Dickson, A. and Goyet, C, (1994), DOE Handbook of Methods for the Analysis of the
Various Parameters of the Carbon Dioxide System in Sea Water, Version 2.
13. Drinking Water Inspectorate, available at http//www.dwi.gov.uk, accessed during
September 2012.
14. Ellis, K.V., (1989), Surface water pollution and its control” Macmillan press Ltd,
Hound mill, Basingstoke, Hampshire RG 21 2xs and London, 3-18, pp 97,100,101
and 208.
15. Gnana Rani, D. F., Arunkumar, K., Sivakumar, S. R., (2005), Physio-chemical
analysis of waste water from cement units, Journal of Industrial Pollution Control,
21(2), 337-340.
16. Gran, G., (1952), Determination of the equivalence point in potentiometric titrations.
Part II. Analyst, 77,pp 661-671.
17. Gupta, D. P., Sunita and J. P. Saharan, (2009), Physiochemical Analysis of Ground
Water of Selected Area of Kaithal City (Haryana) India, Researcher, 1(2), pp 1-5.
18. Hari, O. S., Nepal, M. S. Aryo, and N. Singh. (1994), Combined effect of waste of
distillery and sugar mill on seed germination, seeding growth and biomass of okra.
Journal of Environmental Biology, 3(15), pp 171-175.
19. Hemkes, O. J, Kemp, A, Van, B. L.W., (1980), Accumulation of heavy metals in the
soil due to annual dressings of sewage sludge, New Zealand Journal of Agricultural
Sciences. 28, 228-238.
20. Hopkinson, C.S, (1985), Shallow-water and pelagic metabolism: Evidence of
heterotrophy in the near-shore Georgia Bight, Marine Biology, 87, pp 19.
21. Indian Standard Specification for Drinking Water; IS: 10500: 1992. (Reaffirmed
1993)
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1205
22. Jena, P. K., Mohanty, M, (2005), Processing of liquid effluents of mineral processing
industries, Intl Symposium Environ Manag Mining Metallurgical Industries, 11-14 ,
Bhubaneshwar, pp 193- 212.
23. Karanth, K. R, (1987), Groundwater Assessment Development and Management Tata
McGraw Hill publishing company Ltd., New Delhi, pp 725-726..
24. Kataria, H. C., Quershi, H. A., Iqbal, S. A. and Shandilya, A. K, (1996),Assessment
of water quality of Kolar reservoir in Bhopal (M.P.). Pollution Research. 15(2), pp
191-193.
25. Kodarkar, M. S., (1992), Methodology for water analysis, physico-chemical,
Biological and Microbiological Indian Association of Aquatic Biologists Hyderabad,
Pub. 2 : pp. 50.
26. Krishnamurthy, R., (1990), Hydro-biological studies of Wohar reservoir Aurangabad
(Maharashtra State) India, Journal of Environmental Biology, 11(3), 335-343.
27. Kulkarni, G. J., (1997), Water supply and sanitary engineering. 10th Ed. Farooq Kitabs
Ghar. Karachi, 497.
28. Manjare, S. A., S. A. Vhanalakar and D. V. Muley, (2010), Analysis of water Quality
using Physico-Chemical parameters Tamdalge Tank in Kolhapur District,
Maharashtra, International Journal of Advanced Biotechnology and Research, 1(2), pp
115-119.
29. Milacron Marketing Co., The Effects of water Impurities on Water-Based Metal
working fluids, Technical Report No. J/N 96/47.
30. Misra, S. G., Dinesh, D., (1991), Soil Pollution, Ashing Publishing House, New Delhi,
India
31. Morrissette, D. G., and Mavinic, D. S., 1978. BOD Test Variables. Journal of
Environment: Engg. Division, EP, 6, 1213-1222.
32. Moss, B., (1972), Studies on Gull Lake, Michigan II. Eutrophication evidence and
prognosis, Fresh Water Biology, 2, pp 309-320.
33. National Primary Drinking water regulations, Drinking water contaminants US EPA.
34. Navneet, Kumar, D. K. Sinha, (2010), Drinking water quality management through
correlation studies among various physicochemical parameters: A case study,
International Journal of Environmental Sciences, 1(2), pp 253-259.
35. Pawar, Anusha, C., Nair, Jithender, Kumar, Jadhav, Naresh, Vasundhara, Devi, V.,
Pawar, Smita, C., (2006), Physico-chemical study of ground work samples from
Nacharam Industrial area, Hyderabad, Andhra Pradesh, Journal of Aquatic Biology,
21(1), pp 118-120.
36. Poonkothai, M., Parvatham, R., 2005. Bio-physico and chemical assessment of
automobile wastewater, Journal of Industrial Pollution Control, 21 (2), pp 377-380.
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1206
37. Premlata, Vikal, (2009), Multivariant analysis of drinking water quality parameters of
lake Pichhola in Udaipur, India. Biological Forum, Biological Forum- An
International Journal, 1(2), pp 97-102.
38. Quinn, B. F., Syers, J. K., (1978), Surface irrigation of pasture with treated sewage
effluent, heavy metal content of sewage effluent, sludge, soil and pasture, New
Zealand Journal of Agricultural Research. 21, pp 435-442.
39. Riley, J. P. and G. Skirrow, Eds., Chemical Oceanography, Academic Press, London
and New York.
40. Riordan, O', E. G., Dodd, V. A., Tunney, H., Fleming, G. A, (1983), The chemical
composition of sewage sludges, Ireland Journal of Agriculture Research, 25, 239-49.
41. Robertson, D. E, 1968. Role of contamination in trace
element analysis of sea water. Analytical Chemistry, 40(7), pp 1067-1068.
42. Rokade, P. B., Ganeshwade, R. M., (2005), Impact of pollution on water quality of
Salim Ali Lake at Aurangabad, Uttar Pradesh, Journal of Zoology, 25(2), pp 219-220.
43. Saravanakumar, K. and R. Ranjith, Kumar, (2011), Analysis of water quality
parameters of groundwater near Ambattur industrial area, Tamil Nadu, India, Indian
Journal of Science and Technology, 4(5), pp 1732-1736.
44. Sawane, A. P., Puranik, P. G., Bhate, A. M., (2006), Impact of industrial pollution on
river Irai, district Chandrapur, with reference to fluctuation in CO2 and pH, Journal of
Aquatic Biology, 21(1), pp 105-110.
45. Sharma, Madhvi, Ranga, M. M., Goswami, N. K., (2005), Study of groundwater
quality of the marble industrial area of Kishangarh (Ajmer), Rajshthan, Nature
Environmental and Pollution Technology, 4(3), pp 419-420.
46. Singhal, V., Kumar, A., Rai, J. P. N., (2005), Bioremediation of pulp and paper mill
effluent with Phanerochaete chrysosporium, Journal of Environmental Research,
26(3), pp 525-529.
47. Smith, S.V. and Hollibaugh, J. T, (1993), Coastal metabolism and the oceanic organic
carbon balance, Reviews of Geophysics, 31, pp 75-76.
48. Smith, S.V. and Hollibaugh, J. T, (1997), Annual cycle and interannual variability of
ecosystem metabolism in a temperate climate embayment, Ecology/Ecological
Monographs, 67, 509.
49. Trivedy, R. K., and Goel P. K., (1986), Chemical and biological methods for water
pollution studies, Environmental Publication, Karad, Maharashtra.
50. United States Environmental Protection Agency, (2009), 816-F-09-004.
51. Wang, Z., Wang, Y. and Cai, W.-J. and Liu, S. Y, (2002), A long lathlength
spectrophotometric pCO2 sensor using a gas-permeable liquid-core waveguide,
Talanta, 57, pp 69-80.
Physico-chemical parameters for testing of water A review
Patil. P.N, Sawant. D.V, Deshmukh. R.N
International Journal of Environmental Sciences Volume 3 No.3, 2012
1207
52. WHO Geneva, (2008), Guidelines for drinking-water quality (electronic resource), 3rd
edition incorporating 1st and 2nd addenda, Volume 1, Recommendations.
53. WHO guidelines for drinking water quality. 2nd edition. Recommendation. World
Health organization Geneva, 1, pp 30-113.
... It is obvious that the quality of water in terms of microbiology is subject to changes, and the presence of pathogenic microorganisms in water reduces the safety of the water supply, thereby increasing the risk of diseases caused by, for example, E. coli, Salmonella and Campylobacter bacteria, viruses such as rotavirus and norovirus, and parasites such as Giardia lamblia and Cryptosporidium. Physic chemical contamination resulting from secondary water contamination and posing a risk to the health of water consumers can be divided into contamination resulting from contact of water with materials used to build the network, disinfection by-products (formed from chlorine or hypochlorite and chlorine dioxide), and products of biological and electrochemical corrosion and biofilm contamination [10,26,28,29,[31][32][33][34][35][36][37][38]. The group of threats also includes the interruption of the continuity of water supply, as a result of a failure of the water supply network [35]. ...
... One of the main factors that affects the deterioration of the organoleptic parameters of water is the presence of metal ions in water. One of them is iron, the maximum permissible concentration of which is 0.2 mg/L, while the taste deteriorates at a concentration of 0.05 mg/L [10][11][12]20,25,38]. Water containing iron is characterized by a metallic smell and taste and is cloudy. ...
... Water consumers may also have doubts about the white color of water cloudiness after pouring it into a glass. The most common cause of cloudy water is its aeration, which is not harmful to health [10,38,39]. ...
Article
Full-text available
Various groups of contaminants can be found in water intended for human consumption, such as bacteria, viruses, chemicals, and heavy metals. Many of these contaminants can cause serious health problems, so it is extremely important to ensure that water quality meets current standards. The main objective of this study was to analyze and evaluate the variability of drinking water quality in a selected water supply system located in the southern part of Poland. The results of the research and analysis presented in the study were prepared on the basis of test reports carried out by the water supply company during the operating years 2018–2022. A total of 28 indicators from the group of physicochemical and microbiological parameters were analyzed: color, turbidity, pH, electrical conductivity, nitrates, nitrites, chlorides, chromium, aluminum, cadmium, magnesium, manganese, copper, nickel, lead, mercury, sulfates, total iron, oxidizability, chloroform, total THM (Trihalomethanes), total organic carbon, chlorites and chlorates, Escherichia coli, Enterococci, Coliform Bacteria, Clostridium perfringens (with spores), and total hardness. The results obtained were compared with national and European standards. The analyzed tap water was characterized by a stable physicochemical composition and did not exceed microbiological parameters. The only parameter that would not meet the acceptable value is chromium. Its value in each of the analyzed months was <3.0 μg/L, while the new directive tightens the requirements to 0.25 μg/L. The water supply network operator should take action to reduce the amount of chromium in tap water so that it follows the introduction of new regulations on the quality of drinking water.
... Various natural factors including geological processes, land cover, basin topography, atmospheric precipitation, rock dominance and the evapo-crystallization are affecting the water quality and hydrochemistry of the Himalayan rivers (Pant et al., 2021;Patil, 2015;Ren et al., 2022). ...
... Poor drainage systems, dumping of both treated and untreated sewage and other anthropogenic activities have been the causes of affecting the water quality of the Himalayan rivers (Patil, 2015;Seth et al., 2016). Therefore, the knowledge of water quality and geochemistry is essential to promote effective management of such water resources (Xiao et al., 2014). ...
... Urbanization and pesticide use also spread metal pollutants, worsening contamination . These elements can impact the water's aroma, smell, and looks, as well as how well it supports aquatic life and the health of ecosystems (Patil et al. 2012;Saleem et al. 2019;Nawab et al. 2021). In addition, indicator organisms were detected during heavy metal monitoring. ...
Article
Full-text available
Agricultural water sources are crucial for farming communities and impact both crop health and human consumption. This study examines seasonal variations in the physical, chemical, and bacterial properties of agricultural water sources to understand its effects onpublic health and agricultural productivity. Water samples were collected from various agricultural wells during different seasons throughout the year. Parameters such as pH, temperature, turbidity, TDS, phosphates, nitrates, and heavy metals were analyzed, along with bacterial content, including E. coli and total coliforms. The water quality varied significantly year-round, according to the results, because of factors like rainfall and agricultural runoff. The findings indicated that variables like rainfall and agricultural runoff caused notable annual fluctuations in the quality of the water. Recommendations include improved filtration systems and agricultural practices to ensure safe water for both farming and human use. Bangladesh J. Sci. Ind. Res. 59(4), 205-222, 2024
... The water desalination process is one way to convert seawater into drinking water. It transforms seawater into clean water by separating salt or minerals from seawater to produce fresh water (Patil et al., 2012;Rosyad et al., 2020). ...
Article
Full-text available
The clean water crisis in Indonesia has recently increased due to wastewater pollution in groundwater. As an alternative, the use of seawater for clean water needs to be developed, considering that Indonesia has a very abundant area of sea water which is an alternative as a raw material for clean water resources. In this study, we fabricated TiO2 nanoparticles (NPs) embedded in CA/PEG/Chitosan membranes for seawater desalination. The effect of TiO2 NPs for high-performance of developed membranes was evaluated by reverse osmosis (RO) method to determine the unique characteristics and performance of membranes material for evaluating seawater desalination process. Preparation of CA/PEG/Chitosan membrane-embedded TiO2 NPs was evenly dispersed into the CA/PEG/Chitosan membrane interlayer by blending method and printed on a glass surface to obtain a thin film developed membranes. The characterization and performance over developed membranes were evaluated to observe unique characteristic by adding TiO2 NPs and its high-performance to reject salt content in seawater. Based on these results, the developed membranes were interestingly characterized by using FTIR spectrophotometer shows the presence of functional groups for organic and inorganic bonds such as C = O, -CH3, NH2, C-O, -OH, C-H, and Ti–O-Ti. The presence of TiO2 NPs indicates the attachment of TiO2 NPs in the membranes. In addition, a scanning electron microscope (SEM) was also confirmed to evaluate the morphological structure of without and CA/PEG/Chitosan-modified TiO2 type (I) and (II), in which the pore size of CA/PEG/Chitosan is larger than membrane-embedded TiO2 NPs. Moreover, XRD analysis also confirmed that TiO2 NPs has shown amorphously structures formed on CA/PEG/Chitosan membrane, in which the TiO2 NPs crystal size with 0.25 g of 2.87 nm and 0.5 g of 3.05 nm. Determination of seawater desalination and water flux has shown Ca/PEG/Chitosan membrane-modified TiO2 NPs can increase salt rejection value but reduce membrane water flux value. The highest flux value is 29.4 L/m indicates by CA/PEG/Chitosan membrane, while the salt rejection value is 61.76% from CA/PEG/Chitosan membrane-embedded 0.5 g TiO2 NPs. This study provides a new idea for preparing highly permeable and seawater desalination membranes of CA/PEG/Chitosan membrane-embedded TiO2 NPs under the reverse osmosis method for producing clean water resources.
... Particularly, organic dyes dumped by the textile industry are carcinogenic and hazardous to aquatic life. In order to treat polluted water, several physico-chemical and biological processes have been used [1]. However, these contaminants are recalcitrant to commonly applied processes. ...
Article
Full-text available
This study investigates the efficiency of silica-supported NiFe2O4 nanoparticles as a magnetically recoverable photocatalyst for degrading basic fuchsin pollutants. Ni–Fe/SiO2 nanocomposites were easily synthesized by wet impregnation followed by calcination (T = 350–700 °C). The structural and optical study of Ni–Fe/SiO2 calcined at 700 °C (Ni–Fe(700)) revealed the formation of nanosized spinel phase NiFe2O4 with an average size of 12 nm, a high specific surface area (147 m²g⁻¹), and a narrow band gap of 1.67 eV. Moreover, NiFe2O4/SiO2 nanoparticles exhibited superparamagnetic behavior with a magnetic susceptibility of 1.9 × 10⁻² and a high saturation magnetization (47 emu g⁻¹). These unique properties enable superior photocatalytic performances and easy magnetic separation. Under optimized conditions (dye concentration: 10 ppm, catalyst concentration: 0.1 g L⁻¹, pH = 6), the nanoparticles achieved a remarkable 99% degradation efficiency of basic fuchsin within 40 min, with a pseudo-first-order rate constant of 0.1198 min⁻¹ and a substantial reduction in total organic carbon from 134 to 11 mg L⁻¹ (92%). This high effectiveness, combined with demonstrated recyclability over four cycles, highlights the nanoparticles’ strength and durability. Furthermore, NiFe2O4 nanoparticles are effective across a wide range of pH levels, making them highly adaptable for various environmental conditions. Oxidant radical scavenger experiments permit to identify the superoxide anion radical (●O2⁻) as crucial in the oxidative degradation process, indicating that NiFe2O4/SiO2 acts as reduction photocatalyst. This work highlighted the primordial role of silica, not only as dispersing and stabilizing agent, but also as an actor in the photocatalytic process. Due to its negative electric charge, the adsorption of. cationic dye molecules and the charge separation are improved, while the electron–hole recombination is reduced. The synthesis of stable, highly photoactive, recyclable NiFe2O4/SiO2 offers a sustainable solution for treating dye-polluted wastewater, thereby eco-friendly practices in industrial applications. Graphical Abstract
... The assessment of chemical status is classically based on a list of priority pollutants such as polycyclic aromatic hydrocarbons (e.g., anthracene and naphthalene), biocides (e.g., atrazine and chlorpyrifos), industrial compounds (e.g., benzene, chlorinated alkanes), and metals (e.g., copper and cadmium). Their environmental concentrations are required to remain within levels defined as safe for the environment by European standards (environmental quality standards, EQS) (Patil et al. 2012). The list of priority substances in the water sector and their sources for the marine environment is detailed in Supplementary Information 1 (SI1). ...
Article
Full-text available
Preserving the oceans is a major challenge for the twenty-first century. In 2000, the Water Framework Directive harmonized European regulations on water management to protect and restore the good ecological status of aquatic ecosystems, including the marine environment. This study aims to address the need to understand how pollutants affect marine ecosystems, particularly microbial communities, which are vital for ecosystem balance and biogeochemical cycling. By combining genetic and phenotypic approaches, we aimed to predict the long-term ecological effects of marine pollution and develop improved management strategies. We used microcosms to expose a marine microbial community to various toxicant (anthracene, benzene, chlorpyrifos, copper chloride, and PFOA) and combined phenotypic and genetic approaches to assess i) changes in community structure, ii) phenotypic responses to pollutant, and iii) the benefits of integrating these methods to better evaluate the impact of pollutants on microbial communities and ecosystem services. The obtained results highlight a certain functional resilience despite a significant effect on genetic diversity. Moreover, only specific exposure conditions, such as higher pollutant concentrations, appear to significantly affect ecosystem functions. Leveraging this knowledge, the future challenge will be to develop a straightforward biosensor to estimate and predict the impact of pollutants on these ecosystems, in order to better protect them. Graphical abstract
Article
Full-text available
Spring and well waters are among the most important sources of drinking water in Gofa Zone rural areas; therefore, it is vital to evaluate the quality of these water sources. Hence, this study aims to determine the physicochemical parameters and metallic mineral concentration with its associated health risks of drinking water in selected rural areas of the Gofa zone, Ethiopia. The purposive sampling method was used for water sample collection. Standard analytical procedures were used to determine the physicochemical parameters and mineral contents. The average values of all physicochemical parameters of spring and well-drinking water of the selected areas were obtained as temperature (20.73°C and 20.30°C), pH (7.2 and 6.07), electrical conductivity (481.13 µS/cm and 584.24 µS/cm), dissolved oxygen (4.09 and 6.07 mg/L), turbidity (1.60 NTU and 6.55 NTU), total dissolved solids (330.83 and 338.3 mg/L), total suspended solids (84.76 and 89.24 mg/L), chloride concentrations (58.15 and 60.47 mg/L), SO4²⁻ ion (68.50 mg/L and 5.58 mg/L), NO3⁺ ion (3.25 and 2.75 mg/L), and fluoride ion concentration (0.49 mg/L and 0.37 mg/L). Health risk assessment indicates that Co metal showed high hazard indices compared with Fe, Cu, and Zn. Additionally, the values of the heavy metal pollution index (MPI) and heavy metal evaluation index (HEI) indicate that the Sawla Kusti spring water (SSW5), Geze Gofa Mhirzho Wola spring water (GGSW7), and Geze Gofa Bulki Guya well water (BGWW8) sources are considered highly polluted and not recommended for drinking purposes.
Article
Full-text available
Măng tây (Asparagus officinalis L.) là loại thực phẩm giàu dinh dưỡng, có giá trị kinh tế cao và phù hợp để phát triển nông nghiệp bền vững. Tuy nhiên, ở đồng bằng sông Cửu Long, sản lượng măng tây vẫn còn thấp do điều kiện thổ nhưỡng và mực thủy cấp cao. Nghiên cứu được thực hiện nhằm tuyển chọn công thức phối trộn giá thể có bổ sung nấm rễ nội cộng sinh AMF giúp cải thiện sinh trưởng và năng suất măng tây trong điều kiện canh tác nhà màng. Thí nghiệm được bố trí hoàn toàn ngẫu nhiên với 7 nghiệm thức và 5 lần lặp lại cho mỗi nghiệm thức. Kết quả cho thấy, giá thể sinh học 3XB (4: 1: 1: 4) có nguồn gốc từ 40% phụ phế phẩm trồng dưa lưới ủ hoai phối trộn với nấm rễ AMF + 10% cát + 10% tro trấu + 40% đất mặt đã hỗ trợ sinh trưởng, phát triển và năng suất măng tây. Khối lượng chồi măng tây tươi ở nghiệm thức này tăng 85,24% và khác biệt có ý nghĩa thống kê so với nghiệm thức đối chứng canh tác theo phương pháp truyền thống. Sự tận dụng phụ phế phẩm trồng dưa lưới ủ hoai kết hợp với chủng nấm rễ AMF phối trộn cát, tro trấu và đất theo tỉ lệ (4: 1: 1: 4) làm giá thể trồng măng tây có tiềm năng ứng dụng trong điều kiện canh tác nhà màng.
Article
Full-text available
This study enhances the prediction of biochemical oxygen demand (BOD5), a vital water quality parameter, by developing hybrid artificial neural network models integrated with advanced optimization algorithms. Data from two monitoring stations in South Korea were used to create five models, including the innovative ANN-Enhanced Runge Kutta (ANN-ERUN) model. ANN-ERUN achieved the highest accuracy, significantly outperforming other models. At Gong station, it reduced prediction error (root mean square error: 1.24 mg/L; mean absolute error: 0.83 mg/L) and achieved a determination coefficient of 0.857. Models using eight water quality parameters, including dissolved oxygen and chemical oxygen demand, exhibited superior performance. These findings confirm the effectiveness of ANN-ERUN in precise BOD5 prediction, offering a robust tool for environmental monitoring and sustainable water quality management.
Article
Hard water is an environmental and technical challenge caused by high concentrations of calcium (Ca²⁺) and magnesium (Mg²⁺) ions, leading to scale formation that affects the efficiency of household and industrial appliances and increases maintenance and treatment costs. Additionally, hard water can pose health risks and reduce its quality for daily use. This study aims to evaluate the effectiveness of different doses of sodium hydroxide (NaOH) in treating water hardness and improving water quality by reducing total hardness (TH) and adjusting the physicochemical properties of water. Three main dosages were tested: the first dosage (5 g/L of NaOH), which assessed the basic effectiveness of sodium hydroxide; the second dosage (2.5 g/L of NaOH and 2.5 g/L of Na₂CO₃ with HCl and acid), aimed at balancing hardness reduction with mineral retention; and the optimized dosages (10, 20, and 30 mg/L of NaOH), which proved to be the most effective and balanced. The optimized doses successfully reduced total hardness to levels compliant with Algerian standards while maintaining calcium and magnesium concentrations within acceptable ranges. Furthermore, electrical conductivity (EC) remained within safe limits without significant increases, ensuring the water did not become oversaturated with dissolved salts. The slight increase in sodium (Na⁺) concentration also remained within permissible levels, enhancing the water's suitability for drinking and other uses. Based on these results, the optimized NaOH dosages are the optimal solution for water hardness treatment, achieving a balance between reducing hardness and ensuring water quality in compliance with local standards.
Article
In a long term field experiment 0, 6, 12 or 18 tonnes/ha/yr of sewage sludge (dry matter basis) were applied to permanent grassland. Sludge application markedly increased the contents of Cd, Pb, Zn, Cu, Ni, Cr, Mo, to a depth of 15-25 cm, but Co, Mn and Fe contents were increased only in the surface 5 cm of soil. (Abstract retrieved from CAB Abstracts by CABI’s permission)
Article
Evidence is presented, from studies on deoxygenation of the hypolimnion and from examination of the diatom frustules in a surface mud core, that Gull Lake is becoming progressively more fertile. This appears to be a recent phenomenon, having begun in the last century. Phosphate is identified, from bioassay experiments, as the key nutrient limiting to algal growth. Probable future changes in the lake are discussed, and the existence of `natural' eutrophication is denied.
Article
Studies on seasonal variations in physico-chemical parameters were carried out. The physico-chemical variables studied were atmospheric temperature, water temperature, humidity, dissolved oxygen, oxidizable organic matter, pH, bicarbonate, chloride, sulphate, total nitrogen, phosphate and total solids. An analysis of the seasonal variations of ciliates was carried out in relation to the selected physico-chemical variables.
Article
Physico- chemical and microbiological studies of automobile wastewater in Nammakkal, Tamilnadu, India indicated that the values for pH, EC, TDS, TH, BOD, COD, Calcium, Chloride, Sulphate, Bicarbonate, oil and greases were on the higher side of permissible limits of BIS. Microbiological studies revealed the presence of bacteria such as Pseudomonas aeruginosa, Bacillus subtilis, Micrococcus luteus, Klebsiella sp. and fungal species such as Rhizopus, Mucor, Fusarium, A. niger, A. terreus, Curvularia and Pencillium sp. at high concentration and these organisms serves as indicators for pollutants. MPN test carried out with these samples were found to be positive, for coliforms.
Article
Various Physico-chemical parameters such as D.O., alkalinity, hardness, turbidity and BOD were studied on the samples drawn from the river, "Koel", "Shankha" and " Brahmani" selecting strategic points, almost quarterly over a period of one year in 2002. The quality of water was assessd by estimating dissolved metals such as Ca, Mg, Fe, Pb, Cd and Cr using standard methods and calibrated apparatus. It was observed that dilution during rainy season decreases the metal concentration level to a considerable extent. However the enrichment of these metals by bio-magnification and bio-accumulation in edible components produced in water is accepted to produce a remarkable effect on the water of the river " Brahamani" which is of deep public concern.
Article
The present study was undertaken to investigate the combined effect of effluent of distillery and sugar mill at different concentrations viz. 5, 15, 25, 35, 50, 75 and 100 percent (VIV) on seed germination, seedling growth and biomass of Okra. Germination percentage, seedling growth and biomass increased up to 2 percent effluent concentration. Germination was completely inhibited in 100% effluent. Germination was noted in 75 percent effluent, but seedling did not survived. However, the waste water of distillery and sugar mill may be used for irrigation after diluting the effluent to 75 percent.
Article
This paper presents groundwater quality of Ambattur industrial area in Chennai City. Ten different locations were selected for the study and compared. The parameters studied were pH, total alkalinity, total hardness, turbidity, chloride, sulphate, fluoride, total dissolved solids and conductivity. From overall analysis, it was observed that there was a slight fluctuation in the physico-chemical parameters among the water samples studied. Comparison of the physico-chemical parameters of the water sample with WHO and ICMR limits showed that the groundwater is highly contaminated and account for health hazards for human use.
Article
The present investigation was undertaken to study the different organic pollutants present in the Thane creek water. Some Physico chemical analysis of creek water was also simultaneously carried out. Creek water shows high values of BOD and COD which are hazardous to aquatic life, for every sample High tide and Low tide values have been noted. The results further tabulated to find average values. The investigation has been carried out during a period of June 2002 to May 2003.