Comprehensive Guide to Water Filtration Media and Contaminant Removal
Comprehensive Guide to Water Filtration Media and Contaminant Removal
Water filtration is the process of removing unwanted substances from water by passing it through media that trap contaminants while allowing water to flow through. This guide focuses exclusively on water filtration technologies, the media they employ, and the specific contaminants they target.
Mechanical Filtration Media
Sediment Filters
Materials: Polypropylene, polyester, cotton, pleated paper
Contaminants Removed:
- Sediment, dirt, rust particles
- Sand and silt
- Suspended solids
- Large particulates (>5 microns)
- Applications: Pre-filtration in water systems, well water treatment, residential water filtration
- Ratings: Typically measured in microns (1-100 microns)
Microfilters & Ultrafilters
Materials: Ceramic, hollow fiber membranes, polymer sheets
Contaminants Removed:
- Fine particles (0.1-10 microns)
- Bacteria (E. coli, Salmonella)
- Protozoan cysts (Giardia, Cryptosporidium)
- Algae and some viruses
- Applications: Point-of-use water treatment, backpacking water filters
- Mechanism: Physical straining, size exclusion
Chemical Filtration Media
Activated Carbon
Materials: Coconut shell, wood, coal, processed to create a highly porous structure
Contaminants Removed:
- Chlorine and chloramines
- Volatile organic compounds (VOCs)
- Pesticides and herbicides
- Industrial solvents (TCE, PCE)
- Odors and unpleasant tastes
- Some pharmaceuticals
- PFAS (partially, especially with specialized carbon)
- Disinfection byproducts (THMs, HAAs)
- Applications: Drinking water filters, under-sink systems, refrigerator filters
- Mechanism: Adsorption (contaminants bind to the carbon surface)
- Types:
- Activated Carbon (GAC)
- Carbon block
- Catalytic carbon (enhanced for chloramine removal)
Ion Exchange Resins
Materials: Synthetic polymers with charged functional groups
Contaminants Removed:
- Cation Exchange: Calcium, magnesium (water hardness), heavy metals (lead, copper, cadmium)
- Anion Exchange: Nitrates, sulfates, arsenic, fluoride, perchlorate, chromium-6
- Mixed Bed: Combined removal of both positive and negative ions
- Applications: Water softeners, deionization systems, selective contaminant removal
- Regeneration: Using salt (NaCl) for cation resins, caustic soda for anion resins
Zeolites
Materials: Natural or synthetic aluminosilicate minerals with porous structure
Contaminants Removed:
- Ammonia
- Heavy metals
- Radioactive isotopes (especially cesium and strontium)
- Some organic compounds
- Applications: Specialized water treatment, industrial wastewater treatment
- Types: Clinoptilolite, chabazite, mordenite, synthetic zeolites
Biological Filtration Media
Biofilters
Materials: Ceramic rings, plastic biomedia, lava rock, spongesContaminants Removed:
- Ammonia (converted to nitrite, then nitrate)
- Organic waste compounds
- Some pharmaceuticals and pesticides
- Applications: Aquariums, ecological water treatment, constructed wetlands
- Mechanism: Hosts beneficial bacteria (Nitrosomonas, Nitrobacter) that break down waste compounds
Membrane Filtration
Reverse Osmosis (RO) Membranes
Materials: Thin-film composite (typically polyamide)
Contaminants Removed:
- Dissolved salts and minerals (sodium, chloride)
- Heavy metals (lead, mercury, arsenic)
- Fluoride
- Nitrates
- PFAS (per- and polyfluoroalkyl substances)
- Most bacteria and viruses
- Many pharmaceutical compounds
- Microplastics
- Applications: Drinking water purification, desalination
- Limitations: Wastes water, removes beneficial minerals, requires pre-filtration
Nanofiltration Membranes
Materials: Modified polymer membranes
Contaminants Removed:
- Divalent ions (calcium, magnesium)
- Larger molecules (>200-400 Daltons)
- Some pesticides and herbicides
- Color compounds
- Hardness
- Most pharmaceutical compounds
- Applications: Water softening, selective contaminant removal
- Advantages: Lower pressure requirements than RO, higher flow rates
Ultrafiltration Membranes
Materials: Polymer hollow fibers or sheetsContaminants Removed:
- Bacteria and protozoa
- Colloids and suspended solids
- High molecular weight organics
- Proteins and macromolecules
- Microplastics
- Applications: Whole-house filtration, commercial water treatment
- Pore size: Typically 0.01-0.1 microns
Microfiltration Membranes
Materials: Polyvinylidene fluoride (PVDF), polysulfone, ceramics
Contaminants Removed:
- Bacteria
- Large particles
- Suspended solids
- Some viruses when attached to larger particles
- Applications: Pre-treatment for RO, clarification
- Pore size: Typically 0.1-10 microns
Specialized Water Filtration Media
KDF (Kinetic Degradation Fluxion)
Materials: High-purity copper-zinc granules
Contaminants Removed:
- Chlorine
- Heavy metals (lead, mercury, arsenic)
- Iron, hydrogen sulfide
- Algae and fungi
- Applications: Shower filters, whole-house systems, pre-treatment for RO
- Mechanism: Redox reactions
Bone Char
Materials: Charred animal bones
Contaminants Removed:
- Fluoride
- Lead and other heavy metals
- Some organic contaminants
- Applications: Defluoridation of water
- Mechanism: Adsorption and ion exchange
Greensand
Materials: Glauconite mineral coated with manganese oxide
Contaminants Removed:
- Iron and manganese
- Hydrogen sulfide
- Radium
- Applications: Well water treatment, municipal water
- Regeneration: Potassium permanganate
Activated Alumina
Materials: Porous aluminum oxide
Contaminants Removed:
- Fluoride
- Arsenic
- Selenium
- Applications: Specialized water treatment for specific contaminants
- Limitations: Narrow pH range for optimal performance
Birm
Materials: Lightweight manganese dioxide coated media
Contaminants Removed:
- Iron
- Manganese (at higher pH levels)
- Applications: Well water treatment
- Mechanism: Catalytic oxidation of dissolved metals
Disinfection Methods
UV Treatment
Materials: UV-C lamps with quartz sleeves
Contaminants Removed:
- Bacteria
- Viruses
- Protozoa
- Other microorganisms
- Applications: Point-of-entry disinfection, bottling plants
- Mechanism: DNA/RNA damage that prevents reproduction
- Limitations: No residual protection, requires clear water
Chlorination Media
Materials: Calcium hypochlorite, sodium hypochlorite, chlorine tablets
Contaminants Removed:
- Bacteria
- Viruses
- Some protozoa
- Applications: Municipal water treatment, emergency water disinfection
- Mechanism: Oxidation of cellular structures
- Byproducts: Creates disinfection byproducts (DBPs) like trihalomethanes (THMs)
Multi-Stage Filtration Systems
Point-of-Use (POU) Combination Systems
- Sediment pre-filter (5-10 micron)
- Activated carbon block
- Optional specialized media (KDF, bone char)
Contaminants Removed:
- Sediment
- Chlorine
- VOCs
- Lead
- Heavy metals
- Taste and odor
Under-Sink Reverse Osmosis Systems
- Sediment pre-filter
- Carbon pre-filter
- RO membrane
- Post-filter carbon
- Optional remineralization
Contaminants Removed:
- Nearly all contaminants including dissolved solids, heavy metals, and fluoride
Whole-House Treatment Systems
- Sediment pre-filter
- Carbon filtration
- Optional UV disinfection
Contaminants Removed:
- Sediment
- Chlorine
- Some VOCs
Emerging Water Filtration Technologies
Graphene Filters
Materials: Single-atom thick carbon sheets
Contaminants Removed:
- Dissolved salts
- Heavy metals
- Organic contaminants
- Bacteria and viruses
Advantages:
- High flow rates
- Lower energy requirements than RO
Electrochemical Filtration
Materials: Conductive carbon materials with applied voltage
Contaminants Removed:
- Heavy metals
- Microorganisms
- Organic contaminants
- Applications: Point-of-use water treatment
Advantages:
- Regenerable in place
- Selective removal
Magnetic Nanoparticles
Materials: Iron oxide nanoparticles with functional coatings
Contaminants Removed:
- Heavy metals
- Radionuclides
- Specific targeted contaminants
- Applications: Groundwater remediation
Advantages: Retrievable and reusable
Filter Selection Considerations
Water Quality Factors
- Source water analysis
- Primary contaminants of concern
- pH and hardness levels
- Presence of oxidizers (chlorine)
Performance Metrics
- Flow rate capacity
- Pressure requirements
- Contaminant reduction percentages
- Certification to NSF/ANSI standards
Practical Considerations
- Installation requirements
- Maintenance needs
- Filter replacement frequency
- Cost of ownership
Effective water filtration relies on selecting appropriate media for the specific contaminants present in your water supply. Many filtration systems combine multiple media types to address a range of contaminants. Understanding the capabilities and limitations of each filtration medium is essential for designing effective treatment systems that provide the desired level of purification while considering factors like cost, maintenance requirements, and environmental impact.
Regular water testing and proper maintenance of filtration systems are crucial for ensuring continued protection against water contaminants.
Contaminants
Chlorine
Chlorine is commonly used in water treatment but can be considered a contaminant for several reasons: Chlorine is added to public water supplies primarily as a disinfectant to kill harmful bacteria, viruses, and parasites. This practice has been crucial in preventing waterborne diseases like cholera and typhoid fever.
Health Concerns:
Formation of disinfection byproducts (DBPs) like trihalomethanes (THMs) and haloacetic acids when chlorine reacts with organic matter
These DBPs have been linked to increased risks of cancer, reproductive problems, and other health issues with long-term exposure
Can cause respiratory irritation when chlorine gas evaporates from hot water
Imparts a distinct chemical taste and smell to water
Many people find chlorinated water unpleasant to drink
Environmental Impact:
Chlorinated water discharged into natural water bodies can harm aquatic ecosystems
Toxic to fish, amphibians, and other aquatic organisms
Other issues:
Can damage rubber seals in plumbing fixtures over time
May interfere with certain industrial processes or home brewing
Methods for Removing Chlorine
Activated Carbon Filtration: Most common and effective method
Reverse Osmosis Systems: Removes chlorine along with other impurities
Ultraviolet Light: Can break down chlorine compounds
Chemical Neutralization: Using substances like sodium thiosulfate
Evaporation: Letting water stand uncovered (takes 24+ hours)
Boiling: Accelerates the evaporation process
While there are legitimate reasons to remove chlorine from drinking water, it’s important to note that the disinfection benefits of chlorine have saved countless lives by preventing waterborne disease. The decision to remove chlorine should consider the source water quality and ensure that proper alternative disinfection is in place if needed. This is why it’s important to leave the chlorine until you’re ready to use it.
THMs
THMs, or Trihalomethanes, are a group of chemical compounds that form as disinfection byproducts (DBPs) when chlorine or other disinfectants used to treat drinking water react with naturally occurring organic matter in the water.
The main THMs that concern water quality include:
- Chloroform (the most common THM)
- Bromodichloromethane
- Dibromochloromethane
- Bromoform
These compounds form when chlorine used for disinfection reacts with organic material like decaying vegetation, algae, or other natural organic matter present in the source water. The reaction typically occurs during the water treatment process.
Health concerns associated with THMs include:
- Potential increased risk of certain cancers with long-term exposure
- Possible reproductive issues including increased risk of miscarriage and birth defects
- Potential liver, kidney, and central nervous system effects
The EPA regulates THMs under the Safe Drinking Water Act, setting a maximum contaminant level (MCL) of 80 parts per billion (ppb) for total THMs in drinking water systems. Water utilities must regularly test and report THM levels and take corrective action if levels exceed regulatory limits.
To reduce THM formation, water treatment facilities may:
- Use Activated carbon in the filtration process.
- Remove organic matter before disinfection.
- Use alternative disinfection methods like UV light or ozone.
Arsenic
Arsenic is a naturally occurring element that poses serious health risks when present in drinking water. It’s considered one of the most significant water contaminants globally.
Sources of Arsenic in Water
Natural Sources:
- Weathering and erosion of arsenic-containing rocks and minerals
- Geothermal activity releasing arsenic into groundwater
- Areas with volcanic bedrock often have higher arsenic levels
Anthropogenic (Human) Sources:
- Mining operations and mine drainage
- Metal processing facilities
- Agricultural use of arsenic-containing pesticides (historically)
- Wood preservatives (primarily before 2004)
- Industrial waste discharge
Health Impacts
Arsenic is particularly concerning because it:
- Is a known carcinogen linked to multiple types of cancer (bladder,lung, skin, kidney, liver, prostate)
- Causes arsenicosis (arsenic poisoning) with symptoms including:
- Skin lesions, hyperpigmentation, and keratosis
- Cardiovascular disease
- Peripheral neuropathy
- Diabetes
- Has no taste, color, or odor in water (undetectable without testing)
- Bioaccumulates in the body over time
- Causes developmental issues in children, including reduced cognitive function
- Has effects that may appear only after years of exposure to low levels
Regulatory Standards
The WHO and EPA have established maximum contaminant levels for arsenic in drinking water:
- EPA standard: 10 ppb (parts per billion)
- WHO guideline: 10 ppb
- Many experts recommend even lower levels (≤5 ppb) for optimal safety
Removal Methods
Arsenic is difficult to remove from water. Effective methods include:
- Oxidation followed by filtration
- Coagulation/filtration processes
- Reverse osmosis systems
- Ion exchange technology
- Activated alumina adsorption
Copper
Copper is an essential micronutrient that becomes problematic at elevated concentrations in drinking water. Unlike arsenic, which is toxic at any level, copper has a more nuanced status as a water contaminant.
Sources of Copper in Water
- Plumbing Infrastructure:
- Corrosion of copper pipes and fixtures
- Leaching from brass fittings (which contain copper)
- More pronounced in water with low pH (acidic) or high carbonate levels
- Natural Sources:
- Weathering of copper-bearing rocks and minerals
- Natural deposits in soil that interact with groundwater
- Industrial Sources:
- Mining operations and mine drainage
- Electronics manufacturing
- Agricultural runoff (copper-based fungicides)
- Industrial waste discharge
Health Impacts
Copper has a dual nature when it comes to human health:
At Normal Levels:
- Essential for blood cell formation and iron metabolism
- Supports nerve function and immune system health
- Required for collagen formation
At Elevated Levels:
- Causes gastrointestinal distress (nausea, vomiting, diarrhea, abdominal cramps)
- Metallic taste in the mouth
- Blue-green staining of plumbing fixtures and laundry
- Can cause liver and kidney damage with long-term exposure
- Particularly problematic for individuals with Wilson’s disease
Regulatory Standards
- EPA Maximum Contaminant Level Goal: 1.3 mg/L (1,300 ppb)
- EPA “Action Level”: 1.3 mg/L (requires water systems to take steps when exceeded)
- WHO guideline: 2 mg/L
Detection Signs
Unlike many contaminants, copper often provides noticeable indicators:
- Blue-green stains in sinks, tubs, and on fixtures
- Metallic taste in water
- Green corrosion on pipes and fittings
Removal Methods
- Water Treatment:
- Activated carbon filtration
- Reverse osmosis systems
- Ion exchange
- Distillation
- Source Control:
- Adjusting water pH (less acidic water is less corrosive)
- Adding corrosion inhibitors to water supply
- Replacing copper plumbing with PEX or other alternatives
- Running cold water for 30-60 seconds before using for consumption
Environmental Impact
While copper is toxic to humans at high concentrations, it’s even more toxic to aquatic life, particularly:
- Fish
- Invertebrates
- Algae (at very low concentrations)
This makes copper pollution in natural waterways especially concerning from an ecological perspective.
The unique aspect of copper contamination is that it’s often introduced after water leaves treatment facilities, making point-of-use testing and treatment particularly important for this contaminant.
Mercury
Mercury and Water Contamination
Mercury contamination in water is a significant environmental and public health concern.
Sources of Mercury Contamination
Mercury enters water systems through both natural and human-caused pathways:
- Industrial activities: Coal-fired power plants, mining operations (especially gold mining), and certain manufacturing processes
- Medical and electronic waste: Improper disposal of products containing mercury
- Natural sources: Volcanic activity, weathering of mercury-containing rocks
- Historical pollution: Legacy contamination from past industrial activities
- Artisanal gold mining: A major source globally, particularly in developing countries
Chemical Forms and Behavior
Mercury exists in water in different forms:
- Elemental mercury: Metallic form that can evaporate and travel through air
- Inorganic mercury compounds: Various salts and minerals
- Methylmercury: The most dangerous form, created when microorganisms in water convert inorganic mercury to organic mercury
The transformation to methylmercury is particularly concerning because:
- It bioaccumulates in aquatic food chains
- It’s highly toxic to humans and wildlife
- It can cross the blood-brain barrier and placental barrier
Health Effects
Mercury exposure from contaminated water and fish can cause:
- Neurological damage and developmental issues
- Kidney damage
- Impaired cognitive function
- Cardiovascular problems
- Reproductive issues
- In severe cases, paralysis, coma, and death
- Developing fetuses and young children are particularly vulnerable.
Detection and Monitoring
Water systems are monitored for mercury using:
- Specialized laboratory testing
- Continuous monitoring systems in high-risk areas
- Fish tissue sampling programs
- Sediment analysis
Methods to address mercury contamination include:
- Chemical precipitation and coagulation
- Adsorption using activated carbon
- Membrane filtration
- Bioremediation approaches
- Phytoremediation (using plants to extract contaminants)
Regulations and Standards
Many regulatory bodies have established limits for mercury in drinking water:
- The WHO guideline value is 0.006 mg/L (6 ppb)
- The US EPA maximum contaminant level is 0.002 mg/L (2 ppb)
Phosphorus
Phosphorus and Water Contamination
Phosphorus contamination in water is a major environmental concern with significant ecological impacts. Here’s a comprehensive overview:
Sources of Phosphorus Contamination
Phosphorus enters water systems through several pathways:
- Agricultural runoff: Fertilizers, manure from livestock operations
- Urban/suburban runoff: Lawn fertilizers, pet waste, detergents
- Industrial discharges: Food processing, manufacturing facilities
- Municipal wastewater: Human waste and phosphate-containing products
- Erosion: Natural weathering of phosphorus-containing rocks and soils
Environmental Impact
Excess phosphorus in water bodies causes:
- Eutrophication: Accelerated growth of algae and aquatic plants
- Harmful algal blooms (HABs): Toxic cyanobacteria that harm wildlife and humans
- Oxygen depletion: As algae die and decompose, they consume oxygen
- Dead zones: Areas where oxygen levels are too low to support aquatic life
- Biodiversity loss: Reduction in fish and other aquatic species
Chemical Behavior
Phosphorus exists in water in different forms:
- Orthophosphate: The most bioavailable form that plants can use directly
- Polyphosphates: Chains of phosphate molecules
- Organic phosphorus: Bound to organic matter
- Particulate phosphorus: Attached to soil particles
Unlike many contaminants, phosphorus typically doesn’t directly harm human health at levels found in water systems.
Detection and Monitoring
Water is monitored for phosphorus through:
- Regular water quality testing in lakes, rivers, and streams
- Satellite monitoring of algal blooms
- Continuous monitoring systems in critical watersheds
- Sediment analysis
Remediation and Management
Methods to address phosphorus contamination include:
- Prevention strategies:
- Precision agriculture and nutrient management
- Buffer zones along waterways
- Improved wastewater treatment
- Stormwater management practices
- In-water treatments:
- Aluminum or iron salts to bind phosphorus
- Aeration systems
- Dredging phosphorus-rich sediments
- Phosphorus-binding materials
Fluoride
Fluoride as a Water Contaminant
Fluoride in water presents a unique case as it can be both beneficial and harmful depending on concentration levels. Here’s a comprehensive overview:
Sources of Fluoride in Water
Fluoride enters water systems through various pathways:
- Natural geological sources: Weathering of fluoride-containing minerals (fluorite, apatite)
- Industrial processes: Aluminum production, phosphate fertilizer manufacturing, semiconductor production
- Intentional addition: Water fluoridation for dental health benefits
- Coal burning: Releases fluoride compounds that can enter water through air deposition
- Mining activities: Especially phosphate mining
Health Effects
The health impacts of fluoride vary significantly with concentration:
- Beneficial effects (0.7-1.2 mg/L):
- Strengthens tooth enamel
- Reduces dental caries (cavities)
- Supports bone development
- Harmful effects (above 1.5-4 mg/L):
- Dental fluorosis: Discoloration and pitting of teeth
- Skeletal fluorosis: Joint pain, stiffness, and bone structure alterations
- Potential neurological effects at very high exposures
- Possible thyroid function impacts
Global Context
Fluoride contamination varies worldwide:
- Naturally high concentrations in parts of India, China, Africa, and the Middle East
- The “fluoride belt” stretches from Syria through Jordan, Egypt, Libya, Algeria, Sudan, and Kenya
- An estimated 200 million people globally are exposed to excessive fluoride
Detection and Monitoring
Fluoride in water is monitored using:
- Ion-selective electrode methods
- Colorimetric methods
- Ion chromatography
- Regular testing in municipal water systems
Treatment and Remediation
Methods to remove excess fluoride include:
- Adsorption: Using activated alumina, bone char, or clay
- Membrane processes: Reverse osmosis, nanofiltration
- Precipitation methods: Adding calcium and phosphate compounds
- Ion exchange: Using specially designed resins
- Electrodialysis: Electric current to separate ions
Regulations and Guidelines
Major regulatory standards include:
- WHO guideline value: 1.5 mg/L
- US EPA maximum contaminant level: 4 mg/L (with a secondary standard of 2 mg/L)
- European Union standard: 1.5 mg/L
Water Fluoridation Controversy
The practice of adding fluoride to water supplies has been controversial:
- Proponents cite significant dental health benefits, especially for disadvantaged populations
- Critics raise concerns about personal choice, potential health effects, and appropriate delivery methods
- Many countries have adopted fluoridation while others have rejected it
Chromium
Chromium is a transition metal that can exist in several oxidation states, but in water, it is primarily found as trivalent chromium (Cr³⁺) and hexavalent chromium (Cr⁶⁺). These two species differ significantly in their chemical behavior, environmental mobility, toxicity, and bioavailability.
Sources of Chromium in Water
Chromium contamination in water can arise from both natural sources and anthropogenic (human-made) activities:
Natural Sources:
- Weathering of chromium-containing rocks (e.g., chromite, FeCr₂O₄)
- Volcanic activity
- Forest fires
Anthropogenic Sources:
- Electroplating and metal finishing industries
- Leather tanning (using chromium sulfate)
- Wood preservation (chromated copper arsenate)
- Pigment and dye production
- Mining and ore refining
- Improper disposal of industrial waste
Chromium Speciation in Water
Trivalent Chromium (Cr³⁺):
- Typically less soluble and less mobile in the environment.
- Forms stable complexes with organic matter and precipitates as Cr(OH)₃.
- Considered an essential micronutrient in trace amounts for humans and animals (involved in glucose metabolism).
- Low toxicity.
Hexavalent Chromium (Cr⁶⁺):
- Highly soluble in water as chromate (CrO₄²⁻), dichromate (Cr₂O₇²⁻), or hydrogen chromate (HCrO₄⁻), depending on pH.
- Extremely toxic, carcinogenic, and mutagenic.
- Not essential to human health.
- High mobility in aqueous environments due to its solubility and weak adsorption to soils and sediments.
Environmental Chemistry and Behavior
Redox Transformations:
- Chromium speciation is highly dependent on redox conditions and pH
- Under oxidizing and alkaline conditions: Cr⁶⁺ is stable
- Under reducing and acidic to neutral conditions: Cr⁶⁺ can be reduced to Cr³⁺
- Microorganisms and organic matter in sediments can mediate these redox transformations
Mobility:
- Cr⁶⁺ is more mobile and can leach into groundwater
- Cr³⁺ tends to adsorb to soil particles or form insoluble hydroxides
Toxicology
Hexavalent Chromium (Cr⁶⁺):
- Carcinogenic via inhalation and ingestion (classified as Group 1 by IARC)
- Causes oxidative stress, DNA damage, and apoptosis
- Acute exposure: Nausea, vomiting, diarrhea, and abdominal pain
- Chronic exposure: Kidney and liver damage, skin ulcers, and increased risk of cancer (especially stomach and lung)
Trivalent Chromium (Cr³⁺):
- Low toxicity due to poor absorption
- Acts as a dietary trace element, though its essentiality is debated
Regulatory Standards
World Health Organization (WHO):
- Maximum allowable concentration of total chromium in drinking water: 0.05 mg/L (50 µg/L)
U.S. Environmental Protection Agency (EPA):
- Maximum contaminant level (MCL) for total chromium (includes both Cr³⁺ and Cr⁶⁺): 0.1 mg/L (100 µg/L)
- No separate federal MCL for Cr⁶⁺, though some states (e.g., California) have proposed stricter limits
Analytical Detection Methods
- ICP-MS (Inductively Coupled Plasma Mass Spectrometry) – highly sensitive for total chromium
- AAS (Atomic Absorption Spectroscopy) – for specific speciation with pre-treatment
- Ion Chromatography (IC) with UV detection – for Cr⁶⁺
- Colorimetric methods (e.g., diphenylcarbazide method for Cr⁶⁺)
Remediation and Treatment Technologies
For Hexavalent Chromium:
- Chemical Reduction: Cr⁶⁺ → Cr³⁺ using reducing agents (e.g., ferrous sulfate, sulfur dioxide, sodium metabisulfite), followed by precipitation
- Ion Exchange: Removes chromate ions using anion-exchange resins
- Adsorption: Activated carbon, iron oxides, or bioadsorbents like chitosan and modified clays
- Reverse Osmosis: Effective but energy-intensive
- Bioremediation: Certain bacteria (e.g., Pseudomonas, Bacillus) can reduce Cr⁶⁺ to Cr³⁺
Cyanuric Acid
Cyanuric acid (CYA), also known as 1,3,5-triazine-2,4,6-triol, is an organic compound commonly associated with swimming pool chemistry, but it can also appear as a water contaminant under certain environmental and industrial conditions.
Chemical Structure and Properties
- Molecular Formula: C₃H₃N₃O₃
- Molecular Weight: 129.07 g/mol
- Structure: A symmetrical triazine ring substituted with three hydroxyl groups.
Physical Properties:
- White, odorless solid
- Melting point: ~330°C (decomposes)
- Slightly soluble in cold water (more soluble in hot water)
- pKa values: ~6.9, 11.4, and 13.5 – indicates weakly acidic behavior
Sources of Cyanuric Acid in Water
Anthropogenic Sources:
- Swimming pools: Used as a chlorine stabilizer (prevents UV degradation of free chlorine)
- Disinfectants: Present in chlorinated isocyanurates (e.g., trichloroisocyanuric acid, dichloroisocyanuric acid)
- Industrial effluents: From plastic and resin manufacturing
- Agriculture: Degradation product of herbicides (e.g., atrazine, simazine)
- Fire retardants and bleach alternatives: Decomposition products can include CYA
Natural Sources:
- Cyanuric acid is not naturally occurring in significant concentrations in the environment but may arise through biodegradation of man-made nitrogen-containing organics
Environmental Fate and Behavior
Solubility and Mobility:
- Cyanuric acid is moderately soluble in water but forms strong hydrogen bonds, leading to low volatility
- It is relatively stable in aquatic environments due to the robustness of the triazine ring
- Not strongly adsorbed to soil or sediment, so it has potential for leaching into groundwater
Persistence:
- Biodegradation occurs, but slowly
- Certain bacteria (e.g., Pseudomonas spp., Arthrobacter spp.) can degrade CYA using cyanuric acid hydrolase to produce ammonia and carbon dioxide
Toxicology and Health Impacts
Toxicity Profile:
- Low acute toxicity in mammals (oral LD₅₀ in rats: >5000 mg/kg)
- Not classified as carcinogenic, mutagenic, or teratogenic
- Can cause gastrointestinal irritation at high doses
- In combination with melamine, CYA can form insoluble crystals that may precipitate in kidneys, leading to renal failure – this interaction was implicated in the 2007 pet food contamination incident
Ecotoxicology:
- Generally low toxicity to aquatic organisms, but chronic exposure data is limited
- Synergistic effects with chlorine degradation products may pose additional risks
Detection and Analysis
Analytical Methods:
- Spectrophotometry (e.g., Melamine-CYA complexation colorimetric assays)
- High-performance liquid chromatography (HPLC) with UV or MS detection
- Ion chromatography
- Gas chromatography-mass spectrometry (GC-MS) after derivatization
Regulatory Guidelines and Standards
- U.S. EPA: No federal drinking water Maximum Contaminant Level (MCL) established
- WHO: No guideline values for CYA in drinking water
- Swimming Pool Guidelines:
- Recommended range: 30–50 mg/L
- Upper limit: ~100 ppm – higher concentrations reduce chlorine effectiveness
- Cyanuric acid in public water supplies is not generally regulated unless introduced through unusual sources
Environmental and Public Health Concerns
Swimming Pools and Recreational Water:
- Excess CYA levels can bind free chlorine, reducing disinfection power and allowing microbial survival.
- Can lead to “chlorine lock”, where chlorine is present but not bioavailable.
Industrial Spills or Improper Disposal:
- Contaminated wastewater can introduce CYA into local surface or groundwater sources
- Long environmental persistence and potential degradation into nitrogen-rich byproducts can impact nitrogen cycling and eutrophication in aquatic systems
Interaction with Other Contaminants:
- In combination with melamine, it poses a risk of nephrotoxicity through the formation of insoluble complexes
- Also relevant in wastewater reuse and greywater systems where breakdown products may accumulate
Treatment and Removal
Conventional Methods:
- Not effectively removed by standard drinking water treatment (e.g., coagulation, sedimentation, filtration)
- Activated carbon: Limited effectiveness
Advanced Treatment:
- Advanced oxidation processes (AOPs): Some degradation via ozone or UV/H₂O₂
- Biological treatment:
- Bioreactors with cyanuric acid-degrading bacteria show promise
- Natural attenuation in soils over time
Pool Water Treatment:
- Partial draining and dilution is the most common method for reducing high CYA concentrations in swimming pools
- Specialized enzymatic additives containing CYA hydrolase are also available
Lead
Lead (Pb) is a heavy metal and a well-known toxic water contaminant. It poses significant risks to human health, especially in children, and persists in the environment without degradation. Lead contamination in water is primarily due to corrosion of plumbing systems and industrial pollution.
Chemical and Physical Properties
- Atomic Number: 82
- Atomic Weight: 207.2 g/mol
- Oxidation States: +2 (Pb²⁺, dominant in water), +4
- Solubility: Poorly soluble in water as metallic lead, but Pb²⁺ ions and lead salts are soluble to varying degrees
- pH Sensitivity: Lead solubility increases in acidic and soft (low mineral content) water
Sources of Lead in Water
Anthropogenic Sources:
- Lead pipes and plumbing (primary source in developed countries)
- Lead service lines (LSLs)
- Lead solder in copper pipes
- Brass or bronze fixtures containing lead
- Industrial discharge
- Battery manufacturing
- Mining and smelting
- Paint and pigment production
- Ceramics and glass industries
- Atmospheric deposition from leaded gasoline (historically), waste incineration, and mining activities
- Contaminated soil runoff
Natural Sources:
- Weathering of galena (PbS) and other lead-containing minerals, though less significant than anthropogenic sources
Chemistry of Lead in Water
Speciation:
In aqueous environments, lead primarily exists as:
- Pb²⁺ (free ion, soluble, highly bioavailable)
- Complexes with inorganic ligands:
- Carbonates (e.g., PbCO₃, Pb(CO₃)₂²⁻)
- Hydroxides (e.g., Pb(OH)₂, amphoteric behavior)
- Chlorides, nitrates, sulfates
- Organic complexes with humic and fulvic acids in natural waters
Solubility and Mobility:
- Lead solubility is influenced by pH, alkalinity, redox potential, and presence of complexing agents
- Low pH and soft water enhance lead dissolution
- In high pH environments, lead can precipitate as Pb(OH)₂ or PbCO₃
Toxicological Profile
Human Health Effects:
- No safe level of lead exposure, especially for children
- Lead mimics calcium and accumulates in bones, teeth, and soft tissues
Acute Exposure:
- Abdominal pain, vomiting, constipation, fatigue, encephalopathy (at high doses)
Chronic Exposure:
- Neurotoxicity: Lowered IQ, attention deficits, behavioral problems (especially in children)
- Nephrotoxicity: Kidney damage
- Cardiovascular effects: Hypertension, arterial stiffness
- Reproductive toxicity: Reduced fertility, miscarriage, preterm birth
- Anemia: Inhibits enzymes in heme synthesis pathway
Children and Pregnant Women:
- Most vulnerable populations
- Lead can cross the placental barrier and affect fetal development
Environmental Effects
- Toxic to aquatic life even at low concentrations
- Accumulates in sediments and benthic organisms
- Bioaccumulation in the food chain
- Can affect enzyme activity, reproduction, and growth in fish and invertebrates
Regulatory Standards
Organization | Maximum Contaminant Level (MCL) for Lead |
---|---|
U.S. EPA | 0.015 mg/L (action level, not a health-based MCL) |
WHO | 0.01 mg/L (10 µg/L) |
EU | 0.01 mg/L |
The U.S. EPA’s Lead and Copper Rule (LCR) requires action if more than 10% of tap water samples exceed 15 µg/L.
Detection and Analytical Methods
- Inductively Coupled Plasma Mass Spectrometry (ICP-MS) – highly sensitive
- Graphite Furnace Atomic Absorption Spectrometry (GFAAS) – widely used
- Anodic Stripping Voltammetry (ASV) – field-portable, sensitive
- X-ray Fluorescence (XRF) – for solids or rapid screening
Water Treatment and Remediation
Corrosion Control:
- Orthophosphate addition – forms insoluble lead phosphate scale inside pipes
- pH/alkalinity adjustment – reduces lead solubility
Point-of-Use (POU) Systems:
- Activated carbon filters – limited effectiveness
- Reverse osmosis (RO) – effective for dissolved lead
- Ion exchange resins – selective for Pb²⁺
Source Replacement:
- Lead service line replacement is the only permanent solution
Environmental Remediation:
- Sediment dredging in contaminated water bodies
- Soil stabilization using phosphate amendments or encapsulation
Summary of Lead Behavior in Water
Property | Characteristics |
---|---|
Mobility | Moderate; increases in acidic, soft water |
Toxicity | High, especially for children |
Persistence | Does not degrade; accumulates in environment |
Bioavailability | High in ionic form |
Treatment Difficulty | Challenging; requires multiple approaches |
Radon
Overview
Radon (Rn-222) is a radioactive noble gas formed from the radioactive decay of radium-226, itself a decay product of uranium-238. It is colorless, odorless, and chemically inert, but radioactively active and potentially hazardous when inhaled or ingested.
Occurrence in Water
- Radon can dissolve into groundwater as it moves through uranium- and radium-rich rocks, particularly granite, shale, and phosphate-bearing formations.
- More common in private wells tapping deep aquifers; not usually present in surface waters due to volatilization.
Health Effects
- Primary risk: Inhalation of radon gas released from water during activities like showering, cooking, and laundry.
- Radon decays to short-lived radioactive progeny (e.g., polonium-218, polonium-214), which emit alpha particles that damage lung tissue.
- Associated with lung cancer – second leading cause after smoking.
- Ingestion risk: Less significant, but internal organ exposure (e.g., stomach) is still a concern.
Regulation and Guidelines
Agency | Recommended Limit |
---|---|
U.S. EPA (proposed) | 300–4,000 pCi/L (action levels) |
WHO | No formal guideline, but risk-based evaluation |
Detection and Treatment
- Detection: Liquid scintillation counting, gamma spectroscopy
- Treatment:
- Aeration systems (effective at removing >99%)
- Activated Carbon (GAC) filters (less preferred due to radioactive buildup in media)
Radium
Overview
Radium (Ra) is a naturally occurring radioactive metal in Group 2 of the periodic table. The most common isotopes in water are Ra-226 and Ra-228.
Occurrence in Water
- Found in groundwater due to dissolution from uranium and thorium ores.
- High concentrations in aquifers rich in granite, phosphate rocks, or shale.
- Tends to adsorb weakly to sediments, making it mobile in water.
Health Effects
- Radiological hazard: Emits alpha, beta, and gamma radiation.
- Mimics calcium: Incorporated into bones, leading to bone cancer, leukemia, and other disorders.
- Long-term ingestion increases risk of skeletal damage and hematological malignancies.
Regulation and Guidelines
Agency | MCL (Maximum Contaminant Level) |
---|---|
U.S. EPA | 5 pCi/L (combined Ra-226 and Ra-228) |
WHO | 1 Bq/L (27 pCi/L) for Ra-226 |
Detection and Treatment
- Detection: Alpha spectrometry, gamma spectroscopy, liquid scintillation counting
- Treatment:
- Ion exchange resins
- Lime softening
- Reverse osmosis
- Co-precipitation with barium sulfate
Hydrogen Sulfide
Overview
Hydrogen sulfide (H₂S) is a colorless, toxic, flammable gas with a characteristic “rotten egg” odor. It forms naturally through anaerobic bacterial activity, particularly sulfate-reducing bacteria (SRB) that convert sulfates to H₂S.
Occurrence in Water
- Common in anaerobic groundwater (e.g., deep wells, confined aquifers)
- Produced in swamps, sewers, oil fields, and geothermal springs
- May be released from decaying organic matter or metal sulfide minerals
Health Effects
- At low concentrations (e.g., <1 ppm in water), mainly a nuisance due to odor and taste.
- At higher concentrations (inhalation), H₂S can:
- Irritate eyes and respiratory tract
- Suppress cellular respiration
- Cause asphyxiation at extreme levels
- Can corrode pipes and plumbing fixtures
Regulation and Guidelines
- No specific MCL by the U.S. EPA (considered a secondary contaminant for aesthetics)
- WHO recommends that water with >0.05 mg/L of H₂S be considered unacceptable for drinking
Detection and Treatment
- Detection: Odor threshold (~0.0005 ppm in air), sulfide ion-selective electrodes, colorimetric kits
- Treatment:
- Aeration (oxidizes H₂S to elemental sulfur or sulfate)
- Activated carbon filtration
- Chlorination followed by filtration (H₂S → sulfur or sulfate)
- Oxidizing agents: Hydrogen peroxide, potassium permanganate
Uranium
Overview
Uranium (U) is a naturally radioactive heavy metal, found in soil, rocks, and groundwater. Its most common oxidation state in water is Uranium(VI) as the uranyl ion (UO₂²⁺). Uranium contamination is both a chemical and radiological hazard.
Occurrence in Water
- Naturally present in areas with granite, shale, and phosphate rocks
- Released from mining, uranium milling, nuclear fuel processing
- Can also enter water from fertilizers and coal combustion waste
Health Effects
- Chemical toxicity: Primary concern is damage to the kidneys (nephrotoxicity) due to heavy metal properties
- Radiological risk: Alpha radiation from uranium isotopes (e.g., U-238, U-234), but less significant than chemical effects
- Long-term ingestion can lead to renal tubular damage
Regulation and Guidelines
Agency | MCL |
---|---|
U.S. EPA | 30 µg/L (0.03 mg/L) |
WHO | 30 µg/L |
Detection and Treatment
- Detection: ICP-MS, laser fluorescence spectroscopy
- Treatment:
- Anion exchange
- Reverse osmosis
- Coagulation/filtration
- Adsorption on iron oxides or activated alumina
Nitrite
Overview
Nitrite (NO₂⁻) is an intermediate in the nitrogen cycle, typically formed by microbial oxidation of ammonia and reduction of nitrate. It is highly reactive and toxic in water.
Occurrence in Water
- Formed during nitrification and denitrification
- Found in:
- Septic system leakage
- Agricultural runoff
- Poorly aerated waters
- Chloraminated drinking water systems (incomplete disinfection)
Health Effects
- Reacts with hemoglobin to form methemoglobin, reducing oxygen transport
- Can cause methemoglobinemia (“blue baby syndrome”) in infants
- Linked to blood and vascular system disorders
Regulation and Guidelines
Agency | MCL |
---|---|
U.S. EPA | 1 mg/L as N (≈3.3 mg/L as NO₂⁻) |
WHO | 0.2 mg/L as NO₂⁻ |
Detection and Treatment
- Detection: Spectrophotometry, ion chromatography
- Treatment:
- Biological denitrification
- Ion exchange
- Reverse osmosis
- Chemical oxidation (to nitrate)
Nitrate
Overview
Nitrate (NO₃⁻) is a stable, highly soluble anion and a major nutrient in ecosystems, but in excess it is a significant contaminant, especially in drinking water.
Occurrence in Water
- Common sources:
- Fertilizer runoff
- Sewage and septic systems
- Animal feedlots
- Decomposing organic matter
- Can leach into groundwater due to its high solubility and mobility
Health Effects
- Also causes methemoglobinemia in infants
- Long-term exposure suspected of links to thyroid dysfunction, diabetes, and potential carcinogenic effects via N-nitroso compound formation
Regulation and Guidelines
Agency | MCL |
---|---|
U.S. EPA | 10 mg/L as N (≈45 mg/L as NO₃⁻) |
WHO | 50 mg/L as NO₃⁻ |
Detection and Treatment
- Detection: UV spectroscopy, ion chromatography
- Treatment:
- Ion exchange
- Biological denitrification
- Reverse osmosis
- Electrodialysis
Sulfite
Overview
Sulfite (SO₃²⁻) is a reduced sulfur oxyanion, often used as a preservative, disinfectant, or oxygen scavenger in industrial water systems. It is rarely found naturally in surface or groundwater.
Occurrence in Water
- Added during:
- Food processing
- Boiler feed water treatment
- Pulp and paper manufacturing
- Occasionally formed from microbial sulfur reduction or chemical processes
Health Effects
- Can cause allergic reactions or asthma attacks in sensitive individuals
- Toxic at high concentrations: may interfere with cellular respiration
- Generally not a widespread environmental concern unless industrial misuse occurs
Regulation and Guidelines
- No EPA MCL; regulated in food more than water
- WHO has no specific drinking water guideline
Detection and Treatment
- Detection: Colorimetric assays (e.g., pararosaniline), titration
- Treatment:
- Oxidation to sulfate (e.g., with chlorine, oxygen)
- Aeration
- Activated carbon filtration
Sulfate
Overview
Sulfate (SO₄²⁻) is a naturally occurring ion formed through oxidation of sulfide minerals and organic sulfur. It is non-volatile, chemically stable, and common in natural waters.
Occurrence in Water
- Found in:
- Groundwater from gypsum (CaSO₄) or anhydrite
- Industrial effluents (mining, tanneries, paper mills)
- Atmospheric deposition from fossil fuel combustion
- Not typically hazardous in moderate amounts
Health Effects
- High concentrations (>500 mg/L) may cause:
- Laxative effect (especially in non-acclimated individuals)
- Dehydration
- Unpleasant taste
- Not known to be carcinogenic or systemically toxic
Regulation and Guidelines
Agency | Secondary Standard (non-enforcable) |
---|---|
U.S. EPA | 250 mg/L (aesthetic concern) |
WHO | 500 mg/L |
Detection and Treatment
- Detection: Gravimetric analysis, ion chromatography
- Treatment:
- Reverse osmosis
- Ion exchange
- Lime softening (for CaSO4)
Bromine
Overview
Bromine (Br2) is a halogen similar to chlorine but more reactive in some contexts. In water, bromine is typically introduced as a disinfectant or can form disinfection byproducts (DBPs) such as bromate (BrO₃⁻) when reacting with ozone.
Occurrence in Water
- Naturally present in seawater and brackish groundwater
- Used in pool disinfection, industrial cooling towers
- Bromide (Br⁻) is naturally occurring, and ozonation or chlorination can oxidize it to bromate
Health Effects
- Elemental bromine (Br2) is corrosive and irritating
- Bromate is a probable human carcinogen (Group 2B, IARC)
- Chronic exposure may cause:
- Kidney effects
- Central nervous system toxicity (at high doses)
- Carcinogenicity (animal evidence)
Regulation and Guidelines
Agency | MCL for Bromate |
---|---|
U.S. EPA | 0.010 mg/L (10 µg/L) |
WHO | 0.010 mg/L |
Detection and Treatment
- Detection: Ion chromatography, UV absorbance
- Treatment:
- Minimize bromide in source water
- Control ozonation conditions
- Activated carbon, reverse osmosis
Zinc
Overview
Zinc (Zn²⁺) is an essential trace element for humans but can become problematic in water at high concentrations, mostly due to aesthetic concerns (taste, color, corrosion).
Occurrence in Water
- Natural weathering of zinc ores (e.g., sphalerite – ZnS)
- Industrial sources: galvanized pipes, brass fittings, mining runoff
- Present in some corrosion control chemicals
Health Effects
- Nutritionally essential in small amounts
- High doses (>3–5 mg/L) can cause:
- Metallic taste
- Stomach cramps, nausea, vomiting
- Low toxicity relative to other metals
Regulation and Guidelines
Agency | Secondary Standard (non-enforcable) |
---|---|
U.S. EPA | 5.0 mg/L |
WHO | 3.0 mg/L |
Detection and Treatment
- Detection: Atomic absorption spectroscopy (AAS), ICP-MS
- Treatment:
- Ion exchange
- Reverse osmosis
- Lime softening
Sodium Chloride (NaCl)
Overview
Sodium chloride (NaCl) is common table salt. While not toxic at low levels, elevated concentrations in water can lead to taste, corrosion, and health issues in specific populations.
Occurrence in Water
- Natural mineral deposits, rock salt (halite)
- Road de-icing runoff
- Water softeners
- Seawater intrusion into groundwater
Health Effects
- High sodium can contribute to hypertension in sensitive individuals
- High chloride causes:
- Salty taste
- Corrosion of plumbing and appliances
Regulation and Guidelines
Agency | Recommend Levels (non-enforceable) |
---|---|
U.S. EPA | 250 mg/L (chloride) |
WHO | No health-based limit; <200 mg/L (aesthetic) |
Detection and Treatment
- Detection: Ion chromatography, conductivity
- Treatment:
- Reverse osmosis
- Electrodialysis
- Distillation
Manganese
Overview
Manganese (Mn) is a naturally occurring metal in soil and rocks. While essential in trace amounts, excess manganese in drinking water is a neurotoxicant and can cause aesthetic problems.
Occurrence in Water
- Present in groundwater, especially under reducing conditions
- Common in deep wells, mining regions, or iron-rich aquifers
Health Effects
- Excess intake may cause:
- Neurological effects (especially in infants and children)
- Parkinsonian symptoms with chronic exposure
- Stains laundry, plumbing, and water fixtures
- Can promote biofilm growth in pipes
Regulation and Guidelines
Agency | MCL / Secondary Standard |
---|---|
U.S. EPA | 0.05 mg/L (aesthetic); Health Advisory: 0.3 mg/L |
WHO | 0.1 mg/L |
Detection and Treatment
- Detection: Colorimetric methods, AAS, ICP-OES
- Treatment:
- Oxidation–filtration (e.g., chlorine, permanganate)
- Greensand filtration
- Reverse osmosis
Aluminum
Overview
Aluminum (Al³⁺) is the most abundant metal in the Earth’s crust. It is used in water treatment as a coagulant (aluminum sulfate – alum). While not highly toxic, it is a concern for neurological health and aesthetic quality.
Occurrence in Water
- Alum-treated water supplies
- Leaching from acidic soils or bauxite-rich formations
- Industrial discharge
Health Effects
- High levels (>0.2 mg/L) linked to:
- Possible neurological issues (suspected link to Alzheimer’s, though evidence is inconclusive)
- Bone and kidney damage at extremely high exposure
- Causes discoloration, turbidity, and metallic taste
Regulation and Guidelines
Agency | Guideline (non-enforceable |
---|---|
U.S. EPA | 0.05–0.2 mg/L (secondary standard) |
WHO | 0.2 mg/L (operational) |
Detection and Treatment
- Detection: AAS, ICP-OES, colorimetry
- Treatment:
- pH adjustment and filtration
- Ion exchange
- Reverse osmosis</li>
Iron
Overview
Iron (Fe) is a common element in Earth’s crust, and it occurs in two oxidation states in water:
- Ferrous (Fe²⁺): Soluble, colorless
- Ferric (Fe³⁺): Insoluble, forms rust-colored precipitates
Occurrence in Water
- Naturally present in groundwater, especially anaerobic aquifers
- Can also be introduced from corroding iron pipes
- Promotes biofilm and iron bacteria growth in plumbing
Health Effects
- Not toxic at typical concentrations
- High levels cause:
- Metallic taste
- Staining of laundry and plumbing
- Support of bacterial slime formation
Regulation and Guidelines
Agency | Guidance Level |
---|---|
U.S. EPA | 20 mg/L (health advisory for sensitive populations) |
WHO | 200 mg/L (aesthetic only) |
Detection and Treatment
- Detection: Colorimetry, AAS, ICP-OES
- Treatment:
- Aeration + filtration
- Oxidizing agents (chlorine, ozone, permanganate)
- Ion exchange
- Greensand filters
Sodium
Overview
Sodium (Na⁺) is a naturally occurring element and an essential nutrient but can be a concern in drinking water at elevated levels, especially for individuals with hypertension or sodium-sensitive conditions.
Occurrence in Water
- Natural sources: Weathering of rocks, saltwater intrusion
- Human activities:
- Road salt runoff
- Water softeners (ion exchange with NaCl)
- Industrial effluents
Health Effects
- Generally safe for most people
- At-risk groups: Those with high blood pressure, kidney disease, or heart conditions
- May contribute to hypertension if consumed in excess
Regulation and Guidelines
Agency | Guidance Level |
---|---|
U.S. EPA | 20 mg/L (health advisory for sensitive populations) |
WHO | 200 mg/L (aesthetic only) |
Detection and Treatment
- Detection: Flame photometry, AAS, ICP-OES
- Treatment:
- Reverse osmosis
- Distillation
- Electrodialysis
Hardness
Overview
Water hardness refers to the concentration of calcium (Ca²⁺) and magnesium (Mg²⁺) ions. It affects water’s ability to lather with soap and contributes to scale formation in pipes.
Occurrence in Water
- Results from the dissolution of limestone (CaCO3) and dolomite (CaMg(CO3)2)
- Common in groundwater and hard rock aquifers
Health Effects
- Not a health risk
- May provide beneficial minerals (calcium, magnesium)
- Aesthetic and operational problems:
- Soap inefficiency
- Boiler scaling
- Skin dryness
Classification
Hardness (mg/L as CaCO3) | Classification |
---|---|
0–60/td> | Soft |
61–120 | Moderately hard |
121–180 | Hard |
>180 | Very hard |
Treatment
- HydroFLOW
- Ion exchange (water softeners)
- Reverse osmosis
Benzene
Overview
Benzene (C6H6) is a volatile organic compound (VOC), known for being a carcinogenic industrial solvent and component of petroleum products.
Occurrence in Water
- Leaks from underground fuel storage tanks
- Petroleum refining, chemical plants
- Cigarette smoke and automobile emissions may contribute to atmospheric deposition
Health Effects
- Group 1 carcinogen (IARC) – linked to leukemia
- Other effects:
- Bone marrow suppression
- Immune system depression
- Anemia
Regulation and Guidelines
Agency | MCL |
---|---|
U.S. EPA | 0.005 mg/L |
WHO | 0.01 mg/L |
Detection and Treatment
- Detection: GC-MS, purge-and-trap methods
- Treatment:
- Activated Carbon
- Air stripping
- Reverse osmosis
Toluene
Overview
Toluene (C6H5CH3) is a solvent derived from crude oil, used in the manufacture of paints, thinners, and adhesives.
Occurrence in Water
- Industrial discharges
- Fuel spills and underground tank leaks
- Degradation of petroleum hydrocarbons
Health Effects
- Short-term: Dizziness, nausea, fatigue
- Long-term: Liver and kidney damage, neurological effects
- Not classified as a human carcinogen
Regulation and Guidelines
Agency | MCL |
---|---|
U.S. EPA | 1.0 mg/L |
WHO | 0,7 mg/L |
Detection and Treatment
- Detection: GC-MS
- Treatment:
- Air stripping
- Activated carbon
- Bioremediation
Xylene
Overview
Xylene (C6H4(CH3)2) refers to three isomers (ortho-, meta-, para-) and is used as a solvent in the rubber, paint, and leather industries.
Occurrence in Water
- Petroleum contamination
- Industrial discharge
- Improper disposal of paints and solvents
Health Effects
- Neurological effects (dizziness, confusion)
- Liver and kidney damage
- Not considered a significant carcinogen
Regulation and Guidelines
Agency | MCL |
---|---|
U.S. EPA | 10 mg/L |
WHO | 0.5 mg/L |
Detection and Treatment
- Detection: GC-MS
- Treatment:
- Air stripping
- Activated carbon filtration
- Advanced oxidation
PFAS (Per- and Polyfluoroalkyl Substances)
Overview
PFAS are a group of synthetic chemicals used for their water, grease, and heat resistance. They include PFOA, PFOS, and GenX. Often called “forever chemicals” due to their environmental persistence.
Occurrence in Water
- Firefighting foams (AFFF)
- Industrial discharge
- Landfills
- Non-stick cookware, textiles, food packaging
Health Effects
- Linked to:
- Thyroid disruption
- Immune suppression
- Cancer (kidney, testicular)
- Liver damage
- Developmental effects in fetuses and children
Regulation and Guidelines
Agency | Limit |
---|---|
U.S. EPA (2023 Proposed) | 4 ng/L for PFOA and PFOS |
WHO | 100 ng/L (PFOS), 100 ng/L (PFOA) |
Detection and Treatment
- Detection: LC-MS/MS
- Treatment:
- Activated Carbon
- Anion exchange resins
- High-pressure nanofiltration or reverse osmosis
Pesticides / Herbicides
Overview
These include a variety of synthetic organic compounds used in agriculture to control weeds, insects, and fungi. Common types: atrazine, glyphosate, 2,4-D, alachlor.
Occurrence in Water
- Agricultural runoff
- Leaching from fields to groundwater
- Improper application or disposal
Health Effects
- Varies by compound:
- Hormonal disruption
- Neurotoxicity
- Carcinogenicity (e.g., atrazine, alachlor)
- Reproductive effects
Regulation and Guidelines
Compound | EPA MCL |
---|---|
Atrazine | 0.003 mg/L |
Glyphosate | 0.7 mg/L |
2,4-D | 0.07 mg/L |
Detection and Treatment
- Detection: GC-MS, LC-MS/MS
- Treatment:
- Activated carbon
- Advanced oxidation
- Membrane filtration
VOCs (Volatile Organic Compounds)
Overview
VOCs are carbon-containing chemicals that easily evaporate into the air. Common VOCs in water include benzene, chloroform, trichloroethylene (TCE), and tetrachloroethylene (PCE)
Occurrence in Water
- Industrial solvents
- Gasoline and dry-cleaning operations
- Leaching from landfills and chemical spills
Health Effects
- Many are carcinogenic or neurotoxic
- Long-term exposure linked to:
- Liver and kidney damage
- Central nervous system effects
- Cancer (especially liver and blood cancers)
Regulation and Guidelines
- Multiple VOCs are regulated individually by the EPA
- Benzene: 0.005 mg/L
- TCE: 0.005 mg/L
- PCE: 0.005 mg/L
Detection and Treatment
- Detection: Purge-and-trap GC-MS
- Treatment:
- Air stripping
- Activated Carbon
- Advanced oxidation processes