Environmental chemistry Study Guide
Study Guide
📖 Core Concepts
Environmental Chemistry – Study of chemical/biochemical processes in natural environments (air, water, soil) and how human or biological activity alters them.
Contaminant vs. Pollutant – Contaminant: any chemical present above natural background. Pollutant: a contaminant that causes harmful effects.
Receptor & Sink – Receptor: medium (soil, organism, fish) that experiences the contaminant’s impact. Sink: material that retains or transforms the contaminant (e.g., carbon sink, sediments).
Baseline Environment – The natural, un‑impacted chemical composition of a system; essential for detecting anthropogenic change.
Key Water‑Quality Indicators – Dissolved Oxygen (DO), Chemical Oxygen Demand (COD), Biochemical Oxygen Demand (BOD), Total Dissolved Solids (TDS), pH, nutrients (N, P), heavy metals.
Analytical Foundations – Quantitative chemical analysis (wet‑chemical, spectroscopic, chromatographic) provides the data for all environmental assessments.
📌 Must Remember
Contaminant ≠ Pollutant – All pollutants are contaminants, but not all contaminants are pollutants.
DO vs. BOD vs. COD
DO = O₂ actually present (mg L⁻¹).
BOD = O₂ required by microbes to degrade organic matter (5‑day test, mg L⁻¹).
COD = O₂ needed to chemically oxidize organics + inorganics (mg L⁻¹).
Heavy Metal Toxicity – Cu, Zn, Cd, Pb, Hg are routinely monitored; even trace ppb levels can be hazardous.
Eutrophication Trigger – Excess N or P → algal bloom → ↓ DO → fish kills.
Analytical “Gold Standards”
Metals: AAS, ICP‑OES, ICP‑MS.
Organics: GC‑MS, LC‑MS (including tandem & high‑resolution).
Regulatory Limits – PAHs often limited to low ppb (µg L⁻¹) because many are carcinogenic.
🔄 Key Processes
Sampling → Preservation → Analysis
Collect water/soil/air sample.
Preserve (acidify, cool, filter) to prevent transformation.
Choose appropriate analytical method (metal vs. organic).
BOD Test (5‑day)
Incubate sealed sample at 20 °C.
Measure DO at start and after 5 days.
BOD = DOinitial – DOfinal.
ICP‑MS Metal Determination
Digest sample (acid digestion).
Nebulize into plasma → ionize → mass‑filter → detect ion current → quantify via calibration curve.
GC‑MS PAH Identification
Extract organics (solid‑phase extraction).
Separate on GC column → ionize in MS → match mass spectra to library.
🔍 Key Comparisons
AAS vs. ICP‑OES vs. ICP‑MS
AAS: single‑element, moderate sensitivity, low cost.
ICP‑OES: multi‑element, higher throughput, detection ppb.
ICP‑MS: ultra‑trace detection (ppt), isotopic info, most expensive.
BOD vs. COD
BOD: biological, slower, only biodegradable organics.
COD: chemical, fast, includes non‑biodegradable organics.
GC‑MS vs. LC‑MS
GC‑MS: volatile, thermally stable compounds (PAHs).
LC‑MS: non‑volatile, polar or thermally labile compounds.
⚠️ Common Misunderstandings
“All contaminants are hazardous.” – Some are benign at current concentrations; toxicity depends on dose and exposure pathway.
Confusing BOD with COD. – BOD measures biological oxidation; COD measures total chemical oxidation.
Assuming AAS can detect trace metals at ppt levels. – It is limited to ppb; use ICP‑MS for ultra‑trace work.
Thinking pH alone tells water quality. – pH is important but must be evaluated with DO, nutrients, and metals.
🧠 Mental Models / Intuition
“Chemical River” Analogy – Imagine a river as a conveyor belt: sources (up‑stream) add chemicals, reactions (mid‑stream) transform them, sinks (down‑stream sediments, biota) remove them. Track each segment to diagnose problems.
Dose‑Response Ladder – Low dose → no effect → sub‑lethal → lethal; helps remember why “contaminant” may not be a “pollutant” until concentration crosses a threshold.
🚩 Exceptions & Edge Cases
Metal Speciation – Toxicity depends on chemical form (e.g., Hg⁰ vs. Hg²⁺). Total metal concentration alone can be misleading.
Delayed Toxicity – Some contaminants (e.g., PCBs) bioaccumulate; effects may appear years later.
Urban Runoff “First‑Flush” – The initial stormwater carries the highest pollutant load; sampling after the first 10 % of runoff may underestimate concentrations.
📍 When to Use Which
Metal analysis → If only a few elements needed → AAS; many elements or low‑level detection → ICP‑OES or ICP‑MS.
Organic pollutant screening → Volatile/thermally stable → GC‑MS; polar, non‑volatile → LC‑MS.
Water‑quality field screening → Portable DO meter, pH probe, colorimetric kits for BOD/COD.
Biological impact → Use bioassays/immunoassays for rapid toxicity; PCR for microbial contamination source tracking.
👀 Patterns to Recognize
High BOD + Low DO → Likely recent organic waste input (e.g., sewage, agricultural runoff).
Elevated nutrients + algal bloom → Nutrient leaching/eutrophication.
Sharp spikes of heavy metals after rain → Urban runoff or storm‑driven sediment transport.
PAH presence without petroleum odor → Subsurface oil seepage or historic spill.
🗂️ Exam Traps
Choosing “BOD” when question mentions “total oxidizable matter.” – Correct answer is COD, not BOD.
Assuming any detectable metal is a pollutant. – Remember pollutant requires adverse effect; trace background levels may be benign.
Mix‑up of analytical acronyms – ICP‑OES ≠ ICP‑MS; the former is emission, the latter is mass spectrometry.
Overlooking “first‑flush” effect in runoff questions. – Answers that ignore the disproportionate pollutant load in early stormwater are usually distractors.
Confusing “sink” with “receptor.” – Sink retains/transforms contaminant; receptor suffers the impact.
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