

GC-ECD System for Halogenated Compounds
卤代化合物分析气相色谱 ECD 系统
- SKU GAC-0002
- Gas Chromatography
- CE (to be confirmed)
- ISO 9001 manufacturing (to be confirmed)
- Radiation source compliance for ⁶³Ni (to be confirmed)
Price on request — FOB / CIF quoted per order
Prices depend on configuration, quantity and destination port.
Key specifications
| Detector type | Micro ECD (⁶³Ni, up to 15 mCi, or pulsed discharge) |
|---|---|
| Minimum detectable level | ≤0.008 pg/s (lindane) |
| Linear dynamic range | ≥10⁴ |
| Detector temperature | up to 400 °C |
| Make-up gas | Nitrogen or argon/5% methane, 20–60 mL/min |
| Oven temperature range | Ambient +4 °C to 450 °C |
By Lab Manufacturers China Technical TeamLast reviewed Standards: USP <621>, USP <467>, Ph. Eur. 2.2.28
What is the GC-ECD System for Halogenated Compounds?
A GC-ECD system uses an electron capture detector that responds selectively to electronegative atoms such as chlorine, bromine and nitro groups. It is chosen for trace analysis of organochlorine pesticides, PCBs and halogenated solvents, reaching picogram to femtogram detection limits that FID cannot achieve.
What is the GC-ECD System for Halogenated Compounds?
A GC-ECD system uses an electron capture detector that responds selectively to electronegative atoms such as chlorine, bromine and nitro groups. It is chosen for trace analysis of organochlorine pesticides, PCBs and halogenated solvents, reaching picogram to femtogram detection limits that FID cannot achieve.
Overview
The micro electron capture detector contains a ⁶³Ni radioactive foil or a non-radioactive pulsed discharge source that emits beta electrons, generating a standing current in a nitrogen or argon-methane make-up gas. Electronegative compounds capture electrons and reduce the current, producing a signal. Sensitivity reaches about 0.01–0.1 pg/s for lindane-type compounds, with a linear range of 10⁴–10⁵, narrower than FID. The system usually runs dual columns of different polarity from one or two inlets to confirm identity, as required by EPA organochlorine pesticide methods. Because ⁶³Ni sources are regulated radioactive materials, laboratories need a radiation license and wipe tests, which is why some users choose non-radioactive alternatives. The detector is sensitive to oxygen and moisture, so high-purity gases, clean liners and careful septa handling are essential to keep the baseline stable.
How does it work?
A gas chromatograph injects a liquid or gas sample into a heated inlet, commonly split/splitless at 150–350 °C, where it vaporizes and mixes with carrier gas such as helium, hydrogen or nitrogen. The vapor passes through a capillary column, typically 15–60 m long, 0.25 mm internal diameter, coated with a polysiloxane or polyethylene glycol film of 0.1–1.0 µm. Analytes partition between gas and film according to volatility and polarity. A programmable oven ramps temperature, often from 40 to 300 °C, eluting compounds in boiling-point order. Detectors respond differently: the flame ionization detector senses carbon-containing compounds, the thermal conductivity detector responds to all gases, the electron capture detector to electronegative halogens, and mass spectrometers give identification. Electronic pneumatic control regulates pressure and flow to keep retention times reproducible.
What are the key features?
- Micro ECD with ⁶³Ni source or non-radioactive pulsed discharge source and heated cell to 400 °C
- Detection limit of about 0.01–0.1 pg/s for organochlorine compounds
- Dual-column, dual-detector configuration for confirmation of pesticide and PCB identity
- Electronic pneumatic control of make-up gas improving baseline stability and response
- Low-bleed column options and deactivated inlet liners minimizing activity toward labile pesticides
What are the technical specifications?
A typical gc-ecd system for halogenated compounds configuration offers detector type of Micro ECD (⁶³Ni, up to 15 mCi, or pulsed discharge), minimum detectable level of ≤0.008 pg/s (lindane), linear dynamic range of ≥10⁴, detector temperature of up to 400 °C, make-up gas of Nitrogen or argon/5% methane, 20–60 mL/min and oven temperature range of Ambient +4 °C to 450 °C. Values are indicative of the product class; the exact figures for each configuration are confirmed on the quotation and the calibration documents supplied with the instrument.
Which applications is it used for?
The GC-ECD System for Halogenated Compounds is used in organochlorine pesticide residues in water and soil, PCB congener analysis, halogenated solvent traces, food pesticide residue monitoring and trihalomethane analysis in drinking water. Across the wider Gas Chromatography class, laboratories also deploy it for residual solvent testing in pharmaceuticals, petrochemical hydrocarbon and purity analysis and environmental volatile organic compounds.
Which standards and certifications apply?
Relevant standards and methods include USP <621>, USP <467>, Ph. Eur. 2.2.28, ASTM D6729, ASTM D5134, US EPA Method 8015, ISO 6974, ChP 0521 and IEC 61010-1. Certification candidates for this model are CE, ISO 9001 manufacturing and Radiation source compliance for ⁶³Ni; each is to be confirmed for the specific configuration before shipment, and certificates are supplied only where they have been issued.
Provide high-purity carrier and detector gases, at least 99.999%, with moisture, oxygen and hydrocarbon traps, and install leak-tight fittings since oxygen damages columns at high temperature. If hydrogen is used, install a hydrogen sensor and follow flammable gas safety requirements. Condition new columns following the manufacturer's procedure and respect maximum temperature limits. Replace septa, inlet liners and O-rings regularly, and trim the column inlet to restore peak shape. Verify oven temperature, flow and detector sensitivity during qualification under USP <1058>. Ventilate exhaust, particularly when analyzing toxic solvents, and keep a stable laboratory temperature for electronic pneumatics.
How do I select the right GC-ECD System for Halogenated Compounds?
Select GC-ECD when targets are halogenated, nitro or organometallic compounds at trace levels. It is unsuitable for hydrocarbons. Specify source type, dual-column configuration, required detection limits, make-up gas supply and regional radioactive source licensing. Consider GC-MS/MS if confirmation by mass is required, since ECD gives retention time only and cannot distinguish co-eluting halogenated species.
How does it compare with other Gas Chromatography variants?
Choose the detector first, because it defines what you can measure. FID covers hydrocarbons, solvents and most organic compounds at ppm to ppb levels; ECD is selective for halogenated pesticides and PCBs at ppt levels; TCD is universal and suits permanent gases and percent-level analysis. Headspace sampling is selected for volatile analytes in solid or liquid matrices without injecting the matrix. Portable GC suits field screening. Then consider inlet type, number of detectors, oven ramp rate, electronic pneumatic control precision, autosampler capacity, and carrier gas availability, since hydrogen generators can replace helium. Confirm software support for regulatory reporting, and compare column compatibility with your validated methods, including ASTM, EPA or pharmacopoeial procedures that specify particular phases and dimensions.
Full specifications
| Detector type | Micro ECD (⁶³Ni, up to 15 mCi, or pulsed discharge) |
|---|---|
| Minimum detectable level | ≤0.008 pg/s (lindane) |
| Linear dynamic range | ≥10⁴ |
| Detector temperature | up to 400 °C |
| Make-up gas | Nitrogen or argon/5% methane, 20–60 mL/min |
| Oven temperature range | Ambient +4 °C to 450 °C |
| Inlet configuration | Dual split/splitless up to 400 °C |
| Peak area repeatability (RSD) | ≤2.0% |
| Data rate | up to 200 Hz |
| Autosampler capacity | 50–150 vials |
Indicative values for this product class. Final specifications are confirmed on the quotation and in the calibration documents supplied with the instrument.
Applications
- Organochlorine pesticide residues in water and soil
- PCB congener analysis
- Halogenated solvent traces
- Food pesticide residue monitoring
- Trihalomethane analysis in drinking water
Key features
- Micro ECD with ⁶³Ni source or non-radioactive pulsed discharge source and heated cell to 400 °C
- Detection limit of about 0.01–0.1 pg/s for organochlorine compounds
- Dual-column, dual-detector configuration for confirmation of pesticide and PCB identity
- Electronic pneumatic control of make-up gas improving baseline stability and response
- Low-bleed column options and deactivated inlet liners minimizing activity toward labile pesticides
Frequently asked questions about GC-ECD System for Halogenated Compounds
A ⁶³Ni ECD contains a sealed radioactive source, so many jurisdictions require registration or a general license, periodic leak tests and controlled disposal. Non-radioactive pulsed discharge ECDs avoid this requirement. Check local regulations before purchase.
ECD gives no structural information, so a single retention time can match several compounds. Running the same sample on two columns of different polarity confirms identity when retention times agree on both, which regulatory methods such as EPA 8081 require.
Oxygen, moisture and column bleed are the main causes. Leaks, exhausted gas traps, contaminated make-up gas and dirty detector cells raise noise and reduce response. Use oxygen and moisture traps, leak-check fittings and bake the detector periodically.
Gas chromatography analyzes compounds that can be vaporized without decomposing, generally with boiling points below about 400 °C and molecular weights under roughly 500 Da. This includes hydrocarbons, solvents, pesticides, fatty acid esters and permanent gases. Polar or non-volatile compounds may need derivatization.
Helium is inert and widely specified in methods, but supply is variable. Hydrogen gives faster separations at optimum linear velocity and can be produced by a generator, but requires safety measures. Nitrogen is cheapest and suits some detectors but gives slower analysis and lower efficiency at high flows.
Split injection vents most of the vaporized sample, typically at ratios of 10:1 to 100:1, to prevent column overload with concentrated samples. Splitless injection transfers nearly the entire sample to the column for trace analysis, but requires solvent focusing and a longer inlet residence time.
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